Chenghao Luoa,
Dan Lia,
Long Huang*a,
Zean Wang*bc,
Jian Zhangb,
Hao Liub and
Zhaohui Liub
aChina Tobacco Hubei Industry Co. Ltd, Wuhan 430040, China
bState Key Laboratory of Coal Combustion, School of Energy and Power Engineering, Huazhong University of Science and Technology, Wuhan 430074, China
cSchool of Mechanical Engineering, Wuhan Polytechnic University, Wuhan 430048, China. E-mail: wangzean@whpu.edu.cn
First published on 5th January 2021
“Heat-not-burn” tobacco with an external heating source is a cleaner alternative to conventional cigarettes due to its lower emission of nicotine, CO and tar in the smoke, and graphite is a promising carbon heating source for a “heat-not-burn” tobacco product yet is not easy to be fired. This work aims to improve the combustion properties of graphite using potassium catalysts. Thermal gravimetric analysis is performed to investigate the combustion properties, and a first-order kinetic model is applied to describe the combustion process. Scanning electron microscopy is used to observe the surface morphology, and the mineral and elemental composition are investigated by powder X-ray diffraction and energy dispersive spectrometry, respectively. The results indicate that the potassium additives can significantly decrease the ignition temperature of the graphite samples by 51–124 °C, and the promotion effects are closely related to the potassium and oxygen content of the additives. Further kinetic analysis implies that K and O can decrease the activation energy required for the oxidation reactions by 45.1% from 194.5 to 106.8 kJ mol−1, thereby improving the graphite combustion. Moreover, potassium can play the role of “O2 transfer”, which can transfer atmospheric oxygen to support graphite combustion. K2CO3 is a suitable catalyst for graphite combustion, and the suggested addition amount is 0.88% in weight.
Currently, the external heating system generally involves electricity (i.e. ‘Juul’ from JUUL Labs, ‘iQos’ from Philip Morris International (PMI), ‘Glo’ from British American Tobacco), carbon (i.e. ‘CHTP’ from PMI, ‘Eclipse’ from RJ Reynolds Tobacco Company (RJR)), and liquid fuel (i.e. ‘Ploom’ from Ploom Tech) heating systems.5,6 The electric-heating system seems to be the most popular HNB tobacco product due to its modern appearance and the lowest amount of pollutants in smoke. Unfortunately, an electric HNB tobacco looks far from conventional cigarettes and is not sure to be widely accepted by conventional cigarette smokers. Moreover, an electric HNB product usually involves an extra charger and plug, which is not convenient for outdoor use because of its poor portability.7 By contrast, for a carbon HNB tobacco product, the carbon fuel and tobacco are capsuled by a stick-shaped paper, making the carbon HNB product look more like a conventional smoking cigarette, which allows the smokers not to change their habits. Hence, the carbon HNB tobacco product aims for the niche between conventional and electric cigarettes,3,8 and the carbon heating sources are receiving increasing attention from the researchers.
Generally, a carbon heating source requires good ignition performance, good thermal conductivity, and persistent burning without harmful emissions. So far, few papers have been found closely related to the research on carbon heating source for HNB products, probably because many research works are funded by the manufacturers, and most HNB manufacturers do not always report their findings in peer-reviewed journals. Fortunately, there are quite a few public patents that can hint at the research trend of the external heating sources in some tobacco companies. For instance, PMI submitted several patents using carbon-based heating sources, i.e. ligno-cellulosic materials,9 active carbon impregnated with transition metals, and sulfur and nitrogen ligation.10 Meanwhile, RJR proposed a carbon-containing fuel for use in HNB tobacco,11 graphite mixed with a metal-containing catalyst (i.e. Fe(NO3)3, Cu(NO3)2, Mn(NO3)2, Zn(NO3)2, etc.).12 Through the comparison among different carbon sources (i.e. activated carbon and ligno-cellulosic material), graphite is a promising and clean carbon source with better thermal conductivity, higher calorific value, and longer combustion duration. However, graphite is not easy to be ignited by a lighter, and it seems very promising if safe and efficient additives can be found to improve the ignition performance of graphite.
Currently, plenty of chemicals (i.e. La2O3, Ca(H2PO4)2, and CeO2) have been used to improve combustion or as additives to upgrade the quality of fuels, including coal,13 biomass,14 and biodiesel.15 However, most of them cannot act as the combustion improver of carbon HNB tobacco due to their harmfulness. Among the non-harmful combustion improvers, sodium (i.e. Na3C6H5O7, NaCl, etc.) and potassium salts (i.e. K3C6H5O7, K2CO3, etc.) exhibit good promotion performance,16 which have been used as combustion improvers of cigarette papers. Moreover, potassium salts are found to be more effective in reducing the amount of smoking tar than sodium salts.17 Hence, a potassium salt could be a better combustion improver in comparison with a sodium salt. However, the performances of different potassium additives (including organic and inorganic ones) on graphite combustion require further evaluation, and their promotion mechanisms are also unknown. Moreover, the addition amount of target potassium salt requires further evaluation and optimization.
This work aims to investigate the performances of varying potassium salts (i.e. K3C6H5O7, KC4H5O5, K2C4H4O6, KOH, KNO3, K2CO3, etc.) on graphite combustion and their promotion mechanisms. Graphite is blended with these potassium salts, and the combustion characteristics (i.e. ignition temperature and activation energy) are investigated by thermal gravimetric (TG) analysis. The dispersion of potassium in graphite is characterized by scanning electron microscopy (SEM) coupled with energy dispersive spectrometry (EDS), and the low-temperature ash (LTA) of the graphite is analyzed by powder X-ray diffraction (XRD). The obtained results can provide experimental support for the preparation of a carbon heating source in HNB tobacco products.
Sample | Combustion improver | Fraction in weight | K mass fraction |
---|---|---|---|
G1 | Graphite | 0.00% | 0.00% |
G2 | Graphite + potassium citrate | 1.00% | 0.38% |
G2-L | 0.78% | 0.30% | |
G2-M | 1.31% | 0.50% | |
G2-H | 1.83% | 0.70% | |
G3 | Graphite + potassium malate | 1.00% | 0.23% |
G3-M | 2.20% | 0.50% | |
G4 | Graphite + potassium tartrate | 1.00% | 0.35% |
G5 | Graphite + potassium hydroxide | 1.00% | 0.70% |
G6 | Graphite + potassium nitrate | 1.00% | 0.39% |
G7 | Graphite + potassium carbonate | 1.00% | 0.57% |
G7-L | 0.53% | 0.30% | |
G7-M | 0.88% | 0.50% | |
G7-H | 1.24% | 0.70% |
Fig. 3 displays the TG and DSC curves of graphite and the mixtures. Obviously, the samples doped with different additives exhibit very similar weight loss and exothermic profiles to those of the pure graphite sample G1. To facilitate understanding, the ignition (Tignition) and burnout temperature (Tburnout), as well as the temperature of maximum weight loss rate (Tmax) are summarized in Table 2 to evaluate the performance of different combustion improvers. Generally, the Tignition, Tburnout, and Tmax all decreased after the addition of potassium salts. Among all the additives, G1 shows the highest Tignition of 704 °C, indicating that pure graphite is the most difficult to be directly fired, and a necessary catalyst is required. Notably, the K2C4H4O6 sample possesses the highest Tignition, Tburnout, and Tmax, and the KNO3 sample exhibits the highest performance. Moreover, the temperatures of G5, G6, and G7 decreased much more than those of G2, G3, and G4, clearly illustrating that inorganic K salts can favor the combustion process much more than the organic K compounds. The detailed mechanism will be discussed later.
Sample | G1 | G2 | G3 | G4 | G5 | G6 | G7 |
Tignition (°C) | 704 | 612 | 645 | 654 | 589 | 580 | 589 |
Tmax (°C) | 782 | 685 | 716 | 730 | 667 | 655 | 666 |
Tburnout (°C) | 819 | 730 | 763 | 772 | 707 | 698 | 706 |
Interestingly, inorganic K additives have significant advantages over organic salts in catalytic combustion, which might be associated with the oxygen species of various K compounds. To further investigate the roles of K and O elements during catalytic combustion, Fig. 5 presents the TG and DSC curves of the graphite samples with several fixed K fractions. Organic K3C6H5O7, KC4H5O5, and inorganic K2CO3 are selected as the additives due to their relatively high performances.
Fig. 6 displays the correlations between the Tignition and K, O fraction of the samples. When graphite is blended with the same additive at different addition amounts, a higher K addition amount undoubtedly corresponds to a lower Tignition. Notably, with the K3C6H5O7 additive, the Tignition decreased by 24 °C from 617 to 593 °C with an increase in the K fraction from 0.30% to 0.50%, while the Tignition only reduced by 4 °C from 593 to 589 °C when the K fraction was continuously elevated from 0.50% to 0.70%, and a similar phenomenon is observed for K2CO3 additive. Therefore, the decline of Tignition does not seem to be proportional to the K fraction increase, probably suggesting that the continuous increase of K amount does not always reduce the ignition temperature if the amount of K additive exceeds the threshold value. Fig. 7 summarizes the ignition temperature of the graphite samples. For the K2CO3 additive, when the K fraction content is elevated from 0.50% to 0.70%, the ignition temperature declined by only 10 °C. Moreover, when the K fractions are equal to 0.50%, the ignition temperature of different samples (G2-M, G3-M, and G7-M) does not simply decrease as the oxygen content increases, suggesting that the effect of oxygen in the catalytic combustion process is very complicated. It could be figured out by the assumption below: K can play the role of “O2 transfer” in the catalytic combustion.18 Covalently bound K and O (K2CO3) can react with atmospheric O2 on the carbon surface to form the active intermediate K2O2, which is produced due to the breaking of the K–O bond in K2CO3.19,20 The active intermediate K2O2 can catalytically oxidize graphite carbon to generate K2O and CO2.21 Subsequently, K2O can further react with atmospheric O2 to form K2O2, thereby providing K2O2 for the next stage graphite oxidation, which can be described by eqn (1)–(4). At the initial stage, atomic O in the additives could combine with potassium compounds to produce K2O2, while it is not easy for the organic O to combine with K since the organic carbocyclic O is much more stable than inorganic O, and it would take more energy (heat) to break the carbon ring structure. As a result, the ignition temperature with inorganic potassium is usually lower than that with an organic potassium additive.
K2CO3 + ½O2 → K2O2 +CO2 | (1) |
2K2O2 + C → 2K2O + CO2 | (2) |
K2O + ½O2 → K2O2 | (3) |
K2O + CO2 → K2CO3 | (4) |
Fig. 6 Correlations between Tignition and K, O fraction (G2-L, G2-M, G2-H, G5, G7-L, G7-M, and G7-H). |
Fig. 8 shows the SEM images of LTA of G1, G2-M, and G7-M. Once the samples are heated to 620 °C, G2-M and G7-M can be ignited but not graphite. In Fig. 8a and b, the unburned graphite presents a layered and dense structure, which has not been damaged by the heating process. Simultaneously, G2-M in Fig. 8c and d exhibits a granular and loose structure, indicating that the structure of the edge is gradually destroyed in the combustion process at 620 °C. Fig. 8e and f displays a cottony and curled structure, which is even fading to white, clearly showing the combustion process with the K additive, and G7-M is burned more completely than G2-M.
f(α) = (1 − α)n | (5) |
(6) |
For a slow heating combustion process, the reaction rate is considered to be controlled by chemical kinetics, and the relationship between the reaction rate and temperature follows the Arrhenius law in eqn (7).
(7) |
Eqn (7) is then processed by using Coats–Redfern method,22 and eqn (8) is obtained for convenient data fitting, where G(α) is determined by integrating the formula in eqn (9). The values of −(E/R) and ln(AR/βE) are obtained from the slope and the intercept of the straight-lines from the linear regression of ln(G(α)/T2) against 1/T. G(α) should be −ln(1 − α) for a first-order kinetic model, which is generally suitable to describe the combustion of coal or biomass.
(8) |
(9) |
Fig. 9 displays the linear regression results of ln(G(α)/T2) against 1/T, and corresponding parameters are summarized in Table 3. The values of R2 indicate that the first-order kinetic model can well depict the combustion process of graphite.
Sample | Slope | Intercept | R2 | E (kJ mol−1) | A (min−1) |
---|---|---|---|---|---|
G1 | −23390 | 8.4247 | 0.996 | 194.5 | 1.07 × 109 |
G2 | −15606 | 2.5254 | 0.999 | 129.7 | 1.95 × 106 |
G3 | −17480 | 3.8289 | 0.998 | 145.3 | 8.04 × 106 |
G4 | −17650 | 3.8263 | 0.996 | 146.7 | 8.10 × 106 |
G5 | −13410 | 0.675 | 0.998 | 111.5 | 2.63 × 105 |
G6 | −12846 | 0.2128 | 0.998 | 106.8 | 1.59 × 105 |
G7 | −14050 | 1.3776 | 0.999 | 116.8 | 5.57 × 105 |
Combustion of G1 requires the maximum E value of 194.5 kJ mol−1, and G6 combustion needs the smallest E of 106.8 kJ mol−1. After the addition of K salts, the activation energy required for combustion sharply reduced from 194.5 to 106.8 kJ mol−1, making the occurrence of reaction much easier.
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