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The catalytic effect of calcium and potassium on CO2 gasification of Shengli lignite: the role of carboxyl

The CO2 gasification of Chinese Shengli lignite (SL) catalysed by K+ and Ca2+ was studied. The results showed that calcium could greatly decrease the gasification reaction temperature of SL, and the gasification reaction rates of acid-treated SL catalysed by calcium were significantly higher than that catalysed by potassium. Kinetic analysis showed that the activation energy of the reaction catalysed by calcium was much lower than that catalysed by potassium, which was the reason for the higher catalytic activity of calcium. Fourier transform infrared characterization showed that, compared with acid-treated SL, the addition of K+/Ca2+ resulted in the significant weakening of C=O bond, and new peaks attributed to carboxylate species appeared. X-ray photoelectron spectroscopy results indicated that the numbers of C=O decreased after the metal ions were added, indicating the formation of metal–carboxylate complexes. Raman characterization showed that the ID1/IG values increased, suggesting more structural defects, which indicated that the reactivity of coal samples had a close relation with amorphous carbon structures. Ca2+ could interact with the carboxyl structure in lignite by both ionic forces and polycarboxylic coordination, while K+ interacted with carboxyl structure mainly via ionic forces.


Introduction
Highly efficient and clean utilization of the low rank coals (LRCs) has attracted wide attention around the world due to the large reserves of LRCs. Catalytic gasification is an important way for the utilization of LRCs. Gasification is a thermal chemical process by which the solid fuels are converted to combustible gases in the presence of different gas atmosphere, including steam, oxygen or carbon dioxide. The coal gasification can be divided into three main steps: pyrolysis, volatile matter reforming, and char gasification, and the last step is considered to be the rate-controlling step because it is kinetically slower compared with the other two steps [1,2]. The pyrolysis and devolatilization steps mainly produce tars and release no significant gases, such as CO, CO 2 , H 2 and CH 4 in the temperature range of 300-5008C. The gasification process takes place at least above 5008C. Although the devolatilization process takes place at the first stage, the volatiles may not be completely removed during the gasification process especially when the gasification agents are insufficient [3,4]. In the gasifier, the devolatilization and gasification take place simultaneously. The major reactions involved in the gasification process include combustion (reaction with O 2 ), Boudouard reaction (reaction with CO 2 ), and steam gasification (reaction with steam) [5]. Char is formed simultaneously with the coal gasification reaction. The reaction between char and H 2 O or CO 2 is the rate-determining step. Comparatively, the reactivity of CO 2 with char is much less than that with steam, especially at temperatures lower than 9008C. So Boudouard reaction is generally considered as the rate-determining step in the gasification process [6]. Increasing the Boudouard reaction rate below 9008C is the key step for low-temperature gasification, which can decrease the energy consumption of the gasification process [7].
Catalytic gasification is one of the most attractive options to achieve low-temperature gasification due to the high gasification reaction rate, the selectivity in reaction pathways, and the useful gas products [8]. Moreover, the costs associated with the gasification and the requirements for the related facilities can be reduced by the catalytic approach [9]. Coal contains alkali metals, alkaline earth metals, and transition metals, such as Na, K, Ca, Mg and Fe [10][11][12][13]. The contents of some of these elements within coals are often lower than 1 wt%, but they present a significant catalytic effect on coal gasification as well as obvious influences on the structures of coals during the gasification process. Alkali and alkaline earth metals were reported to be efficient in promoting CO 2 gasification of coal, and thus adding metal salts as additives during CO 2 gasification of coal has served as a hot topic in the field of coal conversion [14 -16]. Potassium has been reported extensively as an effective catalyst for coal gasification [17][18][19]. Calcium also exhibits considerable catalytic effect on coal gasification [20]. The catalytic effects of potassium and calcium on coal gasification were studied extensively. However, the results about the catalytic effects of potassium and calcium obtained by different researchers were still inconsistent because of the variation in composition and properties of different coals [21]. To the best of our knowledge, most researchers reported that the catalytic effects of potassium on the CO 2 gasification of coal or char are much more remarkable than those of calcium [22 -26]. Only few researchers reported that the catalytic effect of calcium was superior to that of potassium on coal gasification [27,28]. The catalytic gasification of coal using calcium as the catalyst has several advantages over potassium, such as lower costs and corrosiveness, abundant reserves on earth, and facile accessibility.
Recently, our previous studies showed that the catalytic effects of calcium were superior to those of potassium on the gasification of Chinese Shengli lignite (SL) [29,30]. In this work, the interaction between lignite and K þ or Ca 2þ is to be investigated, and the possible mechanisms of the catalysing gasification reaction are attempted to be studied.

Sample preparation
Lignite obtained from Shengli coalfield in Inner Mongolia of China was used as the raw material. The received SL samples contained 47.6% moisture, 7.70% ash, 17.3% volatiles and 27.4% fixed carbons. The sample was ground, sieved to the size fraction of 38-74 mm for further processing, and dried in nitrogen atmosphere at 1058C for 4 h.
The demineralized SL sample was obtained by leaching with hydrochloric acid. Approximately 100 g of SL was mixed with 1000 ml 18% hydrochloric acid aqueous solution and stirred for 12 h at room temperature. The resulting slurry was filtered by a vacuum filter, rinsed repeatedly with distilled water to remove the residue chloride ions, and dried in nitrogen atmosphere at 1058C for 4 h, designated as SL þ . The solution was configured as the ratio of 1 g SL þ and 3 ml acid solution of HF (greater than 40%) and soaked for 12 h. The suspension was filtered and washed with distilled water until pH neutrality and then dried at 1058C for 4 h, denoted as SL þþ . The dried SL and SL þþ were also prepared similar to SL þ . According to the previous results [31], the proximate and ultimate analyses of SL, SL þ and SL þþ are listed in table 1. Demineralized coal samples and mass fraction of the main metal elements are presented in table 2.
The reactivity of the gasification of SL þ and SL þþ is similar [32]. Therefore, the metal-cation-doped SL þ coal samples were used to investigate the catalytic effect of different metals during CO 2 gasification. The dosages of all metal ions were 5 wt% of total coal sample. KOH and Ca(OH) 2 were added to SL þ by the impregnation method, named as SL þ -K and SL þ -Ca.

CO 2 gasification
The CO 2 gasification reaction was evaluated in a CCG-2010 fixed-bed quartz reactor. Figure 1 shows a schematic of the experimental set-up for CO 2 gasification.
The reaction system consists of a steam generator and a fixed-bed reactor that is made of stainless steel (8 Â 350 mm). The reactor is heated by an electric furnace. For each experiment, 150 mg of coal sample was loaded in the central zone of the tubular reactor sandwiched by quartz wool and quartz sand in order to maintain homogeneous temperature. Pressure of the reactor was adjusted to 0.25 MPa by reactant gas (Arþ9%CO 2 ) at a flow rate of 110 ml min 21 . The reactor was heated up from room temperature to 6008C at the heating rate of 158C min 21 , and up to 10008C at 28C min 21 .
The produced gas passed through an ice -water trapper followed by a cooler maintained at 2308C to prevent steam and tar matters from entering into the gas chromatography analyser. The concentrations of H 2 , CO, CO 2 and CH 4 in the off gas were quantitatively analysed by an online gas chromatograph (3420) equipped with a thermal conductivity detector, and the sampling interval was 4 min.
The gas instantaneous release rates (F i ) of H 2 , CO, CO 2 and CH 4 are given by where y H2 , y CO , y CH4 , y CO2 and y Ar are the concentrations (v/v%) of H 2 , CO, CH 4 , CO 2 and Ar respectively, and m 0 (g) is the original carbon mass. The carbon conversion (X ) and gasification rate (r) were calculated using the following equations:  where X is the conversion of the coal samples, t 0 the start of gasification (min), t g the termination of gasification (min), t the reaction time (min) [33]. The catalytic efficiency index (EI) is also indicative of the catalytic performance. The EI of the doped metal is defined as follows:

Characterization methods
The Fourier transform infrared (FTIR) spectra of the samples were recorded in the range of 400-4000 cm 21 by a Nicolet FTIR spectrometer NEXUS670, and the spectral resolution was 4 cm 21 . The potassium bromide and coal samples were dried in an oven at 1058C for 4 h before the FTIR investigation. Through the KBr pellet technique, coal samples and KBr at 1 : 200 were ground together to a fine powder and mixed well. Raman spectroscopy with a 532 nm laser was used to investigate chemical structural changes of different samples. Raman analysis was conducted at room temperature by a Thermo Fisher spectrometer equipped with a DXR detector. The spectra were collected in the range of 500-3500 cm 21 . Raman analysis was performed by the method of baseline drift correction and Gaussian peak-differentiating fitting.
Surface composition of the samples was determined by X-ray photoelectron spectroscopy (XPS) with Al K-a radiation using a PHI-5400 spectrometer from America. The analysis area was 300 Â 300 mm. The degree of vacuum was 3 Â 10 27 Pa. The calibration was performed using the main C1s peak at 284.6 eV.

CO 2 gasification reactivity
The CO 2 gasification was performed in a fixed-bed reactor system. Figure 2a demonstrates that the carbon conversion of CO 2 gasification reaction was enhanced with the increase of the temperature for all lignite samples. The rate of CO 2 gasification reaction of each sample was very low and could be negligible at temperatures lower than 7008C. The CO 2 gasification conversion of SL þ increased to 15% at 9008C, which was much lower than those of SL þ -Ca and SL þ -K. SL þ -Ca was converted almost completely at 8508C, and the conversions of SL þ -K and SL þ were 60% and 10%, respectively.
The carbon conversion rates of CO 2 gasification are shown in figure 2b. The reactivity of the SL þ sample increased slowly with the increasing of the temperature from 600 to 10008C, but the reactivity  of the SL þ -Ca and SL þ -K samples increased much faster. The CO 2 gasification reactivity and reaction rate of SL þ -Ca increased significantly once the temperature was higher than 6008C and reached the maximum at 7508C. Relatively, the CO 2 gasification reaction rate of SL þ -K increased steadily from 600 to 7608C. The doped Ca 2þ and K þ showed obvious catalytic effects on CO 2 gasification of SL þ , and the catalytic effect of Ca 2þ was more obvious. EI is used as a useful parameter for evaluating the catalytic efficiency of doped metal for the CO 2 gasification of lignite samples. It can be seen from figure 2c that the EI of SL þ -Ca was extremely high from 650 to 8008C. The EI of SL þ -K is relatively much lower at the same temperature range.
The above results indicated that calcium exhibited significant catalytic effect on the CO 2 gasification reaction of Shengli lignite. Calcium greatly improved the reactivity and reduced the reaction temperature windows. The added potassium had similar catalytic effect on the CO 2 gasification reaction of SL þ with the inherent minerals. The catalytic effect of calcium on CO 2 gasification reaction is superior to that of potassium.

Kinetic analyses of CO 2 gasification
The rate of the gas -solid reaction in a chemical reaction can generally be expressed by the following equation (3.1) [34]: where k is the reaction rate constant (min 21 ), and n is the reaction index. The Arrhenius equation can be expressed as follows: where R is a gas constant (8.314 J mol 21 K 21 ), E is the activation energy (kJ mol 21 ), T is the gasification temperature (K) and A is a frequency factor (min 21 ).
The activation energy E a and frequency factor A can be calculated from the linear fitting of ln½ðdx=dtÞ ð1=ð1 À xÞ n Þ versus 1=T.
The linear fittings of ln½ðdx=dtÞ ð1=ð1 À xÞ n Þ versus 1=T of SL þ -Ca, SL þ -K, SL and SL þ corresponding to main reaction ranges are illustrated in figure 3. The values of frequency factor A, activation energy E a and linear correlation coefficients R 2 of SL þ -Ca, SL þ -K, SL and SL þ are listed in table 3. The CO 2 gasification activation energies of SL þ -Ca, SL þ -K, SL and SL þ were 115.6, 167.8, 157.9 and 218.4 kJ mol 21 , respectively. The addition of calcium reduces the activation energy of CO 2 gasification reaction by 102.8 and 57.7 kJ mol 21 compared to SL þ and SL, respectively, which might contribute to the significant catalytic effect of calcium on the gasification reaction. The addition of potassium reduced the activation energy of CO 2 gasification reaction by 50.6 kJ mol 21 compared to that of SL þ and slightly higher than that of SL. The activation energy of CO 2 gasification reaction of the SL sample was lower than that of SL þ , which proved the catalytic effect of inherent minerals on the CO 2 gasification of Shengli lignite.

Fourier transform infrared spectroscopy
The interaction between calcium or potassium cations and the inherent oxygen functional group within the lignite samples was confirmed by infrared spectroscopy. The FTIR spectra of the four samples are compared in figure 4a.
All of the samples exhibit a broad transmission band at approximately 3420 cm 21 , which could be attributed to the -OH stretching vibration, and bands at 2923 cm 21 and 2848 cm 21 were resolved into stretching vibrations of aliphatic -CH, -CH 2 , and -CH 3 . A typical 400-2000 cm 21 band in the FTIR spectrum is shown in figure 4b. It may be confirmed that the wavenumbers lower than    21 . The band at 1597 cm 21 could be assigned to the stretching vibration of C-O bonds in a carboxyl structure, which should be between the bands of C-O and C¼O bonds, and could not be clearly distinguished, because they were usually shielded by the oxygen containing functional groups in LRC varieties [35]. The most significant difference of infrared spectra lies in 1250-1750 cm 21 . The FTIR analyses of SL and SL þ samples demonstrated reversible conversion of the metal carboxylate groups to carboxyl groups by the acid treatment. The peak intensities of SL þ and SL þþ were increased at 1700 cm 21 . The addition of Ca 2þ and K þ into SL þ leads to the decrease of the band intensity at the same position because -COOH was transformed into -COOM in the presence of metal ions and the C¼O absorption peak was weakened [36,37]. These results meant that the addition of Ca 2þ and K þ resulted in significant changes of the original C¼O due to the formation of metal-carboxylate complexes. The separation of the FTIR bands (Dv ¼ v as ðCO À 2 Þ À v s ðCO À 2 ÞÞ was indicative of the structure of carboxylate [38]. The calculated Dv for SL þ , SL þ -K and SL þ -Ca are    167, 156 and 143 cm 21 , respectively. The addition of Ca 2þ and K þ results in the decrease of the FTIR band separation Dv due to the metal-carboxylate interactions. It can be postulated that the combination of carboxyl functional groups with potassium in SL þ -K is via ionic configurations because these configurations are very common for alkali metal carboxylates [39]. It is impossible to use the Dv value alone to differentiate either ionic or bridging configuration structures in SL þ -Ca. It was reported that calcium acetate had two types of acetate groups, one of which displayed more covalent character and the other was purely ionic force [40]. So it could be deduced from FTIR band Dv values that the Ca 2þ complexes in SL þ -Ca existed via both covalent bonding and ionic configurations simultaneously [41].

Raman spectroscopy
Raman spectra were also used to investigate the structural changes after adding metal ions. Raman spectra of coal samples are shown in figure 5a. In order to get more detailed carbon skeleton structure of coal, each sample was fitted into five peaks according to the literature [42,43]. The fitting curves of Raman spectrum of SL are shown in figure 5b. Table 4 shows the variation trend of the fitting parameters (I D1 /I G and I G /I all ) with the different metal ion addition. I D1 /I G can be used to characterize the surface defect degree in coal samples. With the increase of I D1 /I G , the graphitization was reduced. The ratio of I G /I all reflects the amount of polyaromatic structure in coal sample. The metal ions combined with the carboxyl groups in the aromatic structure of coal, which affected the stability of polycyclic aromatic hydrocarbons to a certain extent. Therefore, the ratio of I G /I all gradually decreased, and SL þ has the maximum degree of graphitization. The greater the degree of graphitization, the fewer the defects and the more stable the structure. It can be deduced that the amount of defects increased due to the introduction of the metal ions, and the contents of graphite crystal structures decreased compared with SL þ . The reactivity of the SL þ samples was improved by the addition of metal ions. Therefore, it could be postulated that the reactivity of coal samples had a close relation with amorphous carbon structures.

X-ray photoelectron spectroscopy
The main C1s XPS spectrum was used to characterize the surface elemental composition of coals. Figure 6 shows XPS C1s spectra of coal samples and fitting chart diagram of SL þ -Ca. The carbon in   [44,45]. By comparing the C1s spectra of samples, it can be found that the proportion of C -C/C-H had no obvious change after the addition of calcium and potassium. The content of C -O was higher than that of SL þ , which meant that adding calcium and potassium could lower the aromaticity. The content of C¼O also decreased probably due to the formation of the -COOM structure after adding the metal ion, which was proved by the FTIR results. The increase of C -O and COO-might be mainly due to the addition of calcium and potassium cations. The combination of the metals and COO -functional group led to more disorder of the coal structure of the samples.

Possible interaction between K þ or Ca 2þ and the carboxyl structure
Lignite is well known to contain amounts of oxygen, and the basic structure of the coal unit includes the polycondensation of various aromatic rings [46,47], single aromatic ring or heterocyclic rings, and the connected hydroxyl ( -OH), carboxyl ( -COOH), carbonyl (-C¼O), methoxy (-OCH 3 ), as well as metal ions coordinated with oxygen functional group [48]. These basic structural units were connected by bridge bond to give rise to the macromolecular structure, and the cage type three-dimensional structure was formed by hydrogen bonds [49 -54]. Based on the results in this work and the structure of the coal, the possible interaction between K þ or Ca 2þ and the carboxyl structure is shown in figure 7. Demineralized coal sample contained a lot of oxygen-containing functional groups, such as carboxyl group and phenolic hydroxyl. The metal-carboxylate interactions formed when metal ions were added into demineralized coal samples. K þ interacted with the carboxyl structure in lignite in the form of ionic forces, while Ca 2þ interacted with the lignite in the form of both ionic forces and polycarboxylic coordination. The different interaction forms led to different effects on the activation energy of the gasification reaction. The addition of K þ led to the decrease of the activation energy from 218.4 kJ mol 21 (SL þ sample) to 167.8 kJ mol 21 , while the activation energy for Ca 2þ added sample decreased to 115.6 kJ mol 21 . It could be speculated that the lower activation energy for Ca 2þ added samples contributed to the superior catalytic performance compared with K þ during CO 2 gasification reaction.

Conclusion
In summary, the gasification reactivity and the structure changes of different SL samples during CO 2 gasification process were investigated. It was proved that Ca 2þ and K þ could significantly promote the CO 2 gasification, and Ca 2þ exhibited higher activity than potassium. Kinetic analysis indicated that the activation energies of SL þ -Ca, SL þ -K and SL þ samples were 115.6, 167.8 and 218.4 kJ mol 21 , respectively. Detailed characterization showed that K þ interacted with the carboxyl structure in lignite mainly in the form of ionic forces, while Ca 2þ interacted with the lignite in the form of both ionic forces and polycarboxylic coordination. It could be deduced that the different interaction forms of Ca 2þ and K þ with the carboxyl structure in lignite led to the differences in activation energy, and finally resulted in the superior activity of Ca 2þ compared with K þ . It is believed that this result could be applied to all LRC with high oxygen functional group content, especially carboxyl structure.
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