Journal of Radioanalytical and Nuclear Chemistry (2022) 331:5817–5824 https://doi.org/10.1007/s10967-022-08650-1 Study on the radon absorption performance of microwave regenerated activated carbon Xiyu Yang1 · Jian Shan1 · Songbo Tan1 · Fengdi Qin1 Received: 26 August 2022 / Accepted: 27 October 2022 / Published online: 15 November 2022 © Akadémiai Kiadó, Budapest, Hungary 2022 Abstract Activated carbon is widely used in 222Rn removal. Meanwhile, the regeneration of activated carbon is key to improve its utilization in 222Rn removal. The goal of this study is to find the most appropriate conditions of the regeneration of activated carbon for the removal of 222Rn and to provide a reference for the application of microwave-assisted regeneration of saturated activated carbon. In this paper, the self-developed microwave device is used to perform multiple regeneration experiments at different gas flow rates, and the 222Rn absorption coefficient of activated carbon is determined by dynamic adsorption. The relative standard deviation of 3.4% suggests that the measured dynamic adsorption coefficient is stable, reliable, and well reproducible. When the flow rate is 4 L ­min−1, the dynamic adsorption coefficient of 222Rn, generated by the activated carbon after three cycles through open-loop regeneration, reaches the maximum value, around 20.8% higher than the fresh activated carbon. In the closed-loop regeneration mode (6 L ­min−1 flow rate), the dynamic adsorption coefficient is 19.1% higher than that of fresh activated carbon. The aperture characterization shows that the micropores are most abundant ranging from 5 to 6 Å. Moreover, at 8 and 10 L ­min−1, the pore diameter of the activated carbon is in the range of 5 to 6 Å, about 20.0% and 30.0% higher than nine cycles. Therefore, three to four cycles times, using closed-loop regeneration at a low gas flow rate (4 L ­min−1) can improve the 222Rn adsorption and the utilization rate of activated carbon most effectively. Keywords Radon adsorption · Microwave regeneration · Closed-loop regeneration method · Open-loop regeneration method · Dynamic adsorption coefficient Introduction 222 Rn is a colorless and tasteless, natural radioactive gas produced by various decay chains of uranium and thorium. It mainly comes from the soil, building materials, and water, and is also the main source of natural radiation [1]. Aerosols carrying 222Rn and its products inhaled in the respiratory system can damage organs and cause lung cancer. According to the International Agency for Research on Cancer, 222Rn is the second-largest substance that can cause lung cancer [2]. Therefore, its removal from the natural environment is particularly important. Adsorption is widely used in industrial and research practice for the separation of many substances including metals. * Jian Shan shanjian0666@163.com 1 School of Nuclear Science and Technology, University of South China, Hengyang 421001, Hunan, The People’s Republic of China It is also widely used in the removal of harmful air pollutants and toxic volatile organic compounds [3]. In addition, activated carbon also plays an important role in the removal of radionuclides from the environment, such as the removal of U(VI) and Th(IV) ions in water media [4]. At the same time, activated carbon is one of the most common adsorbents used for the removal and reduction of 222Rn removal due to its good adsorption capacity and low production cost [5, 6]. However, when the adsorption of 222Rn reaches the equilibrium state, the saturated activated carbon is unable to adsorb more of it. To reuse activated carbon for continuous 222 Rn prevention, saturated activated carbon will be heated and regenerated. The traditional heating method achieves efficient regeneration through the indirect heating of conduction and convection, mainly depending on the thermal conductivity of the material. This method has the disadvantages of long heating time, uneven heating, and high energy consumption [7]. To widen the application range of the activated carbon adsorption process, more efficient regeneration methods are needed. 13 Vol.:(0123456789) 5818 Journal of Radioanalytical and Nuclear Chemistry (2022) 331:5817–5824 The main difference between microwave heating and traditional heating is the heat generation method. In microwave devices, radiations are converted into heat by dipole rotation and ion conduction [8]. When a high-frequency voltage is applied, the response of the materials with a permanent dipole moment or an induced dipole changes their direction, opposite to the direction of the applied field. Synchronous stirring of the molecule then generates heat. Therefore, microwave heating is fast and has low energy consumption [9–11]. At present, microwave heating is widely applied in the preparation and modification of activated carbon [12], however, only a few studies are reported on the desorption and regeneration of saturated activated carbon through this technology. This study compared the 222Rn adsorption capacity of activated carbon after the open-loop and closedloop regeneration method under different conditions, thus, providing reference for the engineering application and promoting the use of microwave regeneration devices for activated carbon regeneration. material is cylindrical polyTeflon and can load up to 1200 g of activated carbon. Experimental methods Introduction to the experimental equipment The microwave regeneration device was developed by our team. It consists of a cuboid structure of 76 cm long, 63.5 cm wide, and 83.5 cm high. The schematic diagram of the operational principle of the device is shown in Fig. 1. Two microwave generators are operating independently, to achieve the adjustable microwave power of 0 ~ 2100 W. The microwave power of 300 W is used in this study. The device has a side length of 23 cm and a 51 cm high positive eight-sided column furnace with a rotating activated carbon bed bracket, which can hold up to 10 activated carbon beds. The carbon bed Principle of microwave heating and regeneration AN electromagnetic wave has frequencies in the range of 3106 to 3109 Hz. The frequencies of civilian microwaves used for heating are 915 MHz and 2450 MHz. When microwaves encounter different materials, they are reflected, adsorbed, and penetrate the material, depending on the dielectric constant, dielectric loss coefficient, specific heat, shape, and moisture content of the material. The microwave power of activated carbon adsorption is represented by Pc(W)[13, 14]: Pc = P0 ๐ = ๐0 ๐1 E2 ๐f (1) where P0 is the total microwave power, ๐ is microwave absorption efficiency of activated carbon, ๐0 is the dielectric constant of free space, ๐1 is the dielectric loss constant, E is the electric field strength, and f is the electromagnetic field frequency. The number of molecules adsorbed on the surface of the activated carbon depends on the number of colliding molecules with the activated carbon and their residence time on its surface. When the number of colliding molecules that collide with the activated carbon per unit of time is represented by n, their average residence time is represented by ๐ , and the adsorption capacity per unit of the surface area is represented by ๐: ๐ = n๐ (2) The basic equations can be derived from the notion of "ideal" disorder in the molecular theory of gas dynamics: n= 1 n๐ 4 0 0 (3) where ๐0 is the average velocity of all molecules, which varies with temperature and molecular weight, and n0 represents the number of molecules per unit volume. According to the scientific laws of the ideal gas: n0 = Np N = V RT (4) where N is the Avogadro constant, V is the volume per mole, p is the pressure of the ideal gas, R is the gas constant, and T is the absolute temperature. According to the Maxwell velocity distribution law, ๐0 can be acquired by the following formula (5): √ 8RT (5) ๐0 = ๐M Fig.1 Schematic diagram of the microwave regeneration device 13 Journal of Radioanalytical and Nuclear Chemistry (2022) 331:5817–5824 differential equations. When the time is 0, the unit pulse value of the adsorbent mass is shown by the following formula: where M is the molecular weight of the gas. Therefore, according to formulas (4), (5), and (3): n= √ Np 2๐MRT (6) The relation between T and τ was given by Frenkel in 1924: Q ๐ = ๐0 e RT (7) In this equation , τ0 is the vibration period of the molecule in the adsorbed state, Q is adsorption heat, the energy needed to desorb from activated carbon. According to formulas (6), (7), and (2), an expression for the adsorption capacity per unit surface area σ can be obtained: Q Np ๐0 e RT ๐=√ 2๐MRT 5819 (8) In the process of 222Rn adsorption by activated carbon, M and τ0 are constant. When the temperature increases, the 222 Rn gas adsorbed on the activated carbon decrease. Therefore, when heating the 222Rn activated carbon, more 222Rn disorients from the activated carbon as the temperature rises. Yn = nn F n−1 tn−1 (− nFt e kM ) (n − 1)!(kM) (10) When the derivative of (10) is equal to zero, the time required for adsorption mass concentration to reach its maximum value can be obtained as follows: tmax = (n − 1)kM nF (11) Since the concentration curve given by (10) is almost symmetrical, it can be assumed that t­max occurs at the midpoint of the curve. Thus, this value is equivalent to the halfpenetration time (t). At the same time, when n → ∞, n−1 →1, n the dynamic adsorption coefficient k can be obtained using the following equation: k= Ft M (12) Theoretical principle of dynamic adsorption The dynamic adsorption experiment is shown in Fig. 3 The activated carbon was dried in an oven before the measurement. The pumps of Rad7 were open during the process, the “sniff” mode of measurement was set and the measurement period was 5 min. 222 Microwave regeneration experiment dYi −Fn = (Y − Yi+1 ) dt kM i In this study, the activated carbon was adsorbed and regenerated nine times in two modes; open loop and closed loop, as shown in Fig. 4a and b, respectively. Gas-flow rate regulation in the open-loop and closed-loop regeneration methods was 4, 6, and 8 L ­min−1, and 6, 8, and 10 L ­min−1, respectively. A saturated activated carbon sample was placed in the proposed device. After regeneration, 25 g of the material was randomly sampled to measure the adsorption coefficient. Rn adsorption coefficient is a key parameter to characterize the 222Rn absorption capacity of activated carbon. Dynamic adsorption of 222Rn is generally associated with activated carbon. In dynamic adsorption, activated carbon is divided into n-block carbon layers, as shown in Fig. 2. The mass balance of each stage adsorbent is shown by the following formula: (9) In the equation, k is the dynamic adsorption coefficient (L ­g−1), F is the flow rate of the carbon column (L ­min−1), Yi is the volume fraction of adsorbent leaving i th layer in the gas phase, M is the total mass of the adsorbent (g), and t is the time (min). The concentration of the adsorbent along stage n of the carbon column is obtained by solving the n Fig. 2 Schematic diagram of the carbon layer Fig.3 Schematic diagram of the dynamic adsorption experiment of activated carbon for 222Rn 13 5820 Journal of Radioanalytical and Nuclear Chemistry (2022) 331:5817–5824 Fig.4 Schematic diagram of the microwave open-loop regeneration experiment (a) and closed-loop regeneration experiment (b) Results Tendency of dynamic adsorption coefficient with regeneration times Dynamic 222Rn absorption coefficient of fresh activated carbon Dynamic 222Rn absorption coefficient of fresh coconut shell activated carbon is measured five times, which is shown in Table 1. The calculated value is 3.03 ± 0.1 L ­g−1. The relative standard deviation of 3.40% indicates that the 222Rn dynamic adsorption coefficient is stable, reliable, and highly reproducible. It is noted that there is a competition between water and 222Rn molecules during dynamic adsorption. However, 222Rn molecules reach adsorption equilibrium faster than water molecules, therefore, the competitive influence of water molecules can be ignored. Since the 222Rn-containing air entering the activated carbon bed is not removed, the measurement results are slightly lower than the actual value. The trend for the dynamic adsorption coefficient of the openloop and closed-loop regeneration activated carbon absorption of 222Rn with the regeneration times is shown in Fig. 5. The dynamic adsorption coefficient of activated carbon 222 Rn increases and then decreases, and reaches the maximum value after the third or fourth regeneration, however, its maximum value decreases when the flow velocity increases. In the open-loop regeneration method, when the flow rate is 4 L ­min−1, the dynamic adsorption coefficient of activated carbon on 222Rn after three cycles increases by 20.8% compared with fresh activated carbon. When the flow rate is 8 L ­min−1, the dynamic adsorption coefficient of activated carbon decreases to the lowest value by 20.5% compared with fresh activated carbon. In the closed-loop regeneration method, the 222Rn dynamic adsorption coefficient reaches the maximum value, 19.1% higher than fresh activated carbon, after the third regeneration and flow rate of 6 L ­min−1. When the flow rate increases to 10 L ­min−1, the dynamic adsorption Table 1 Measurement results of dynamic adsorption factor of activated carbon 222Rn absorption Activated carbon Quantity (g) Half penetration Air flow rate time (min) (L ­min−1) Dynamic 222Rn absorption coefficient (L ­g−1) Average value Standard bias Relative standard deviation N1 N2 N3 N4 N5 80.50 15.10 25.00 25.00 25.00 285.53 49.12 95.79 85.72 83.73 3.19 2.92 3.06 3.01 2.94 3.03 0.10 3.40% 13 0.90 0.90 0.80 0.88 0.88 Journal of Radioanalytical and Nuclear Chemistry (2022) 331:5817–5824 5821 Fig.5 Variation of dynamic adsorption coefficient with regeneration times in open-loop regeneration method (a) and closed-loop regeneration method (b) coefficient of regenerated activated carbon drops to the lowest value, 4.0% lower than fresh activated carbon. The main reason for the above trend is that the pore structure of activated carbon changes after microwave irradiation. The high heat generated by microwaves collapses the part of the existing pore wall of activated carbon, thereby, producing many new microporous structures, conducive to the adsorption of 222 Rn. Therefore, the dynamic 222Rn absorption coefficient of activated carbon reaches its peak value after three or four times of microwave recycling. When the number of recycling and regeneration increases further, the activated carbon pore wall collapse phenomenon is too intense due to the continuous heat accumulation, and the micropore volume is gradually reduced to the lowest value. In addition, the oxygen content is the main influencing factor in the open-loop and closed-loop regeneration of activated carbon. In the open-loop regeneration method, a large amount of air enters the carbon bed, oxidizing the activated carbon at a high temperature, and part of the activated carbon burns. The phenomenon of charcoal burning is relatively strong, resulting in the serious collapse of activated carbon pores and a reduction in the volume of micropores. However, the oxygen content in the closed-loop regeneration method is limited and the charcoal burning process is less. At the same flow rate, the dynamic adsorption coefficient after multiple regenerations (more than four times) is higher than that of activated carbon after open-loop regeneration. Micromorphological characterization of microwave regenerated activated carbon The micromorphology of fresh activated carbon and microwave regenerated activated carbon are analyzed by using scanning electron microscopy (SEM), as shown in Fig. 6. The activated carbon sample is regenerated three times at an airflow rate of 8 L ­min−1. From the comparison, the pore structure of the activated carbon surface after microwave regeneration is much richer than that of fresh activated carbon, and a large number of attachments in and around pores are also removed after microwave regeneration. In addition, during the microwave regeneration process, the surface of the activated carbon produces many cracks, and most of the occluded pores are also opened. The reason for these changes may be: (1) the activated carbon absorbs microwave energy in the internal "microdomain explosion" which cracks the surface of the activated carbon. (2) Under microwave irradiation, carrying gas flowing through the activated carbon bed may be taken away in the activated carbon pore with subtle impurities, thereby, increasing the microporous volume of activated carbon. Surface characteristic parameters of microwave regenerated activated carbon NXVY represents the activated carbon analysis after the Xth microwave closed-loop regeneration at a gas flow rate of YL·min−1. The surface characteristic parameters of activated carbon after microwave closed-loop regeneration are shown in Table 2. At a gas flow rate of 8 L·min−1, the BET surface area, microporous area, and pore volume of the ninth-cycle regenerated activated carbon are reduced by 5.9%, 5.8%, and 11.1%, respectively, compared with the third regenerated activated carbon. Similarly, at a gas flow rate of 10 L ­min−1, 13 5822 Journal of Radioanalytical and Nuclear Chemistry (2022) 331:5817–5824 Fig.6 SEM images of fresh activated carbon of 20 K times (a), regenerated activated carbon of 20 K times (b), fresh activated carbon of 50 K times (c) and regenerated activated carbon of 50 K times (d) Table 2 Surface characteristic parameters of activated carbon after microwave closed-loop regeneration Samples BET surface area ­(m2/g) Microporous area ­(m2/g) Pore volume ­(cm3/g) N3V8 N9V8 N3V10 N9V10 909.92 855.86 892.68 834.03 749.06 705.12 732.59 687.98 0.38 0.34 0.37 0.32 the BET surface area, microporous area, and pore volume of the ninth-cycle regenerated activated carbon are 6.5%, 6.1%, and 14.4% lower than the third regenerated activated carbon, respectively. At the same flow rate, these parameters of the third-cycle regenerated activated carbon are all higher than that of ninth-cycle regenerated activated carbon. For all the above changes, the most likely reason is that with the increasing number of microwave regeneration cycles, 13 activated carbon internal new micropore wall collapses under continuous high temperature, therefore, the area and volume of micropores show a decreasing trend. This also corresponds well to the trend of the 222Rn dynamic adsorption coefficient of activated carbon, that is, the dynamic adsorption coefficient of activated carbon 222Rn after three to four cycles of regeneration reaches the maximum value. Pore structure of microwave regenerated activated carbon The pore structure of the microwave-assisted closed-loop recycled activated carbon is analyzed by Mack Instruments, USA (3-Flex). N ­ xVy represents the Xth microwave cycle regeneration of activated carbon at a gas flow rate of YL·min−1. The adsorption and desorption isotherm and the aperture distribution curves are shown in Fig. 7. The adsorption isotherm of all activated carbon samples belongs to type I isotherm, and the adsorption process is Journal of Radioanalytical and Nuclear Chemistry (2022) 331:5817–5824 5823 Conclusion reversible, suggesting physical adsorption. And with the increase in relative pressure, the final saturation adsorption amount of the regenerated activated carbon samples is significantly higher than that of fresh activated carbon. This further validates that the adsorption performance of microwave recycling regeneration on activated carbon can improve to a great extent. According to the aperture distribution curve, all samples show the first peak at the aperture width range of 5 Å < d < 6 Å, and a second peak close to 8 Å, however, the value is much smaller than the first peak. When the flow rate is the same, the pore structure after three cycles in this pore size range is significantly more than that after nine times recycling, that is, when V = 8 L ­min−1, 10 L ­min−1, activated carbon after three cycles, the pore increment in aperture range of 5 Å to 6 Å is about 20% and 30% higher than that after nine cycles. At the same gas flow rate, there is an obvious positive correlation between the 222Rn dynamic adsorption coefficient of activated carbon and the pore increment in the aperture range of 5 Å to 6 Å. Moreover, with the increase in the microwave cycle frequency of 222Rn absorption activated carbon, its aperture increased. When the number of cycles is more than three times, with the increasing cycle times, a new microporous hole wall produced in the previous microwave regeneration collapses under the action of high energy, thus, gradually linking adjacent pores together and increasing the pore aperture, which is not conducive to the adsorption of 222Rn. This eventually leads to the phenomenon that after multiple cycles (more than four), the dynamic adsorption coefficient of 222Rn decreases. (a) 350 This study explores the dynamic 222Rn absorption coefficient of microwave open-loop and closed-loop regenerative activated carbon at different flow rates and characterized their pore structure. Combined characterization results of the dynamic adsorption coefficient and the pore structure, the following conclusions are obtained: (1) With the increase in regeneration times, both dynamic 222 Rn absorption coefficient of microwave open-loop and closed-loop regenerative activated carbon show an increasing trend and then decreasing, reaching the maximum value after the third or fourth cycle, and the maximum value decreases with the increase in flow rate. (2) When the number of microwave regeneration cycles and gas flow rate are the same, the dynamic 222Rn absorption coefficient of activated carbon samples obtained by the closed-loop regeneration is higher than that of the open-loop regeneration method. (3) The aperture of activated carbon used is mainly in the order of 5 Å < d < 6 Å and 6.5 Å < d < 10 Å. At an aperture range of 5 Å < d < 6 Å, the content of pore structure is positively related to the dynamic absorption coefficient. (4) The activated carbon samples after three cycles have the highest pore content in the range of 5 Å < d < 6 Å. However, when the cycle is more than three times, the pore aperture range at 5 Å < d < 6 Å becomes larger. (b) 500 250 200 150 N9V8 100 N3V8 N3V10 50 N9V10 N0V0 0 0.0 0.2 0.4 0.6 Relative Pressure (P/Po ) 0.8 1.0 Incremental Surface Area (m²/g) Quantity Adsorbed (cm³/g ) 300 N9V8 N3V10 N3V8 N9V10 N0V0 400 300 200 100 0 4.0 4.5 5.0 5.5 6.0 6.5 7.0 7.5 8.0 8.5 9.0 9.5 10.0 Pore Width (Å) Fig.7 Adsorption and desorption isotherm (a) and aperture distribution curves (b) of different activated carbon samples 13 5824 Therefore, the three to four cycles and closed-loop regeneration method at a low gas flow rate are conducive to improving the micropore content of activated carbon which plays a main role in the 222Rn adsorption process, to obtain the regenerated activated carbon with the best 222Rn adsorption performance. Acknowledgements This study was supported by the National Natural Science Foundation of China (12075112). The authors would like to thank all the reviewers who participated in the review, as well as MJEditor (www.โmjediโtor.โcom) for providing English editing services during the preparation of this manuscript. Declarations Journal of Radioanalytical and Nuclear Chemistry (2022) 331:5817–5824 6. 7. 8. 9. 10. 11. Conflict of interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper. 12. References 13. 1. Grzywa-Celiลska A, Krusiลski A, Mazur J et al (2020) Radon— the element of risk. J Impact Radon Exposure Human Health 8(4):120 2. Maier A, Jones J, Sternkopf S et al (2021) Radon adsorption in charcoal. J Int J Environ Res Public Health 18(9):4454 3. Cherbaลski R, Molga E (2009) Intensification of desorption processes by use of microwaves—an overview of possible applications and industrial perspectives. J Chem Eng Process Process Intens 48(1):48–58 4. 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