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ISSN : 1738-1894(Print)
ISSN : 2288-5471(Online)
Journal of Nuclear Fuel Cycle and Waste Technology Vol.19 No.2 pp.271-278
DOI : https://doi.org/10.7733/jnfcwt.2021.19.2.271

# Recycling of Li2ZrO3 as LiCl and ZrO2 via a Chlorination Technique

Min Ku Jeon1,2*, Sung-Wook Kim1, Keun-Young Lee1, Eun-Young Choi1,2
1Korea Atomic Energy Research Institute, 111, Daedeok-daero 989beon-gil, Yuseong-gu, Daejeon 34057, Republic of Korea
2University of Science and Technology, 217, Gajeong-ro, Yuseong-gu, Daejeon 34113, Republic of Korea
* Corresponding Author. Min Ku Jeon, Korea Atomic Energy Research Institute, E-mail: minku@kaeri.re.kr, Tel: +82-42-868-2435

February 10, 2021 ; March 8, 2021 ; March 12, 2021

## Abstract

In this study, a chlorination technique for recycling Li2ZrO3, a reaction product of ZrO2-assisted rinsing process, was investigated to minimize the generation of secondary radioactive pyroprocessing waste. It was found that the reaction temperature was a key parameter that determined the reaction rate and maximum conversion ratio. In the temperature range of 400−600℃, an increase in the reaction temperature resulted in a profound increase in the reaction rate. Hence, according to the experimental results, a reaction temperature of at least 450℃ was proposed to ensure a Li2ZrO3 conversion ratio that exceeded 80% within 8 h of the reaction time. The activation energy was found to be 102 ± 2 kJ·mol−1·K−1 between 450 and 500℃. The formation of LiCl and ZrO2 as reaction products was confirmed by X-ray diffraction analysis. The experimental results obtained at various total flow rates revealed that the overall reaction rate depends on the Cl2 mass transfer rate in the experimental condition. The results of this study prove that the chlorination technique provides a solution to minimize the amount of radioactive waste generated during the ZrO2-assisted rinsing process.

## 초록

Ministry of Science and ICT

## 1. Introduction

Oxide reduction (OR) is a key process that enables the use of oxide fuels discharged from pressurized water reactors (PWRs) in electrochemical pyroprocessing [1]. Recycling of the metallic fuels, employed in the Experimental Breeder Reactor-II (EBR-II) sodium-cooled fast reactor (SFR), via pyroprocessing was successfully demonstrated in the USA [2]. An integrated system of pyroprocessing and SFR is under intensive research in South Korea with the aim of recycling the transuranic (TRU) nuclides existing in the used nuclear fuels (UNFs) of PWRs as a fuel for SFRs [3-4].

The OR process liberates oxygen atoms from oxide fuels so that the resulting metallic fuels can be processed via subsequent electro-refining and electro-winning processes to recover U and TRU nuclides. Normally, LiCl containing 1−3wt% Li2O is employed as a molten salt in the OR process at around 650℃ [5-8]. In order to construct an electrochemical circuit for the OR process, oxide fuels are loaded into a metal basket to serve as the cathode, with platinum employed as the anode. The reactions occurring at the cathode and anode are listed below:

<Cathode>

(1)

(2)

(3)

<Anode>

(4)

There are two mechanisms, chemical and electrochemical, which explain the reaction behavior at the cathode. In the chemical mechanism, Li metal is generated through reaction (1) and then reacts with UO2 to produce U and Li2O via reaction (2). In the electrochemical mechanism, UO2 is directly converted to U via an electrochemical reaction (3). As the operation potential of the two mechanisms are close, both pathways can occur simultaneously during the OR operation. In the anode, oxygen ions liberated from UO2 are oxidized to O2 gas through reaction (4). Regardless of the cathode reaction mechanism, the overall reaction equation of the OR process can be expressed as reaction (5).

(5)

When the OR operation is complete, the cathode basket is discharged from the reactor along with any residual salt adhering to the metallic fuel and basket. The cathode basket is transferred to a salt distillation process, during which the residual salt is removed by heat and a vacuum to obtain clean metallic fuel [3, 4, 9]. During this process, Li2O dissolved in the residual salt reacts with U metal, resulting in a reoxidation reaction through reaction (6), expressed below, which is a reverse reaction of reaction (2) [10, 11].

(6)

Here, the consistent removal of Li, with a melting point of 454 K and a boiling point of 1615 K, using heat and a vacuum is a key driving force that keeps reaction (6) going. In addition, it was documented that a higher Li2O concentration or distillation temperature can lead to a higher degree of reoxidation [10, 11].

This reoxidation phenomenon will cause a significant reduction in the overall process efficiency, as the reoxidized product, UO2, is not recoverable through electro-refining. Recently, Choi et al. proposed a ZrO2-assisted rinsing process as an alternative to the salt distillation process [12]. In this process, the cathode basket is immersed in a separate bath of molten LiCl such that Li2O in the residual salt is diluted. Here, ZrO2 is utilized as a Li2O scavenger to prevent the accumulation of Li2O in the rinsing bath via the following reaction mechanism [13, 14]:

(7)

Although the rinsing technique was successfully demonstrated through repeated experiments, the reaction product, Li2ZrO3, should be replaced by ZrO2 periodically. The resulting Li2ZrO3 can be handled as a radioactive waste for disposal after several treatments. As a result, the ZrO2- assisted rinsing technique will produce additional radioactive waste, Li2ZrO3, unless it can be recycled. In this work, a chlorination technique was applied to recycle Li2ZrO3 through reaction (8) below, with the goal of recycling LiCl and ZrO2 in the ZrO2-assisted rinsing process.

(8)

## 2. Experimental

The Gibbs free energy change (ΔG) values of the Li2ZrO3 chlorination reaction (reaction (8)) were derived using the HSC chemistry software (version 9.5.1) as a function of the reaction temperature [15]. Chlorination experiments were conducted using a quartz tube reactor with a diameter of 4 cm. The reactor was equipped with an electrical furnace to control the reaction temperature. Before the reaction began, the weight of the Li2ZrO3 powder (Sigma-Aldrich) was measured before and after the sample was loaded into an alumina boat. Approximately 0.50 g of Li2ZrO3 was used for each experiment. The boat was placed in the middle of the quartz reactor and both ends were then connected to a gas control system. On the inlet side of the reactor, a gas feed system with two mass flow controllers (MFCs, Kofloc co., Japan) for Ar (Model 3660) and Cl2 (Model 5440) was connected. A dry scrubbing system for the removal of unreacted Cl2 was connected to the other side of the reactor. After purging the reactor with Ar for at least 2 h, the reactor was heated to the reaction temperature at a ramping rate of 10℃∙min–1 under an argon flow. When the reactor temperature is settled at the target temperature, each MFC was set at the reaction flow rate and then maintained for the reaction time. Upon the completion of the reaction, the Cl2 flow was stopped and the reactor was cooled to room temperature under an argon flow. After discharging the alumina boat, the weight of the sample was measured with or without the alumina boat to quantify the weight change. The highest reaction temperature in this work was set to 600℃ in order to minimize the volatilization loss of LiCl during the reaction. Experiments were repeated for various reaction temperatures (300−600℃), durations, and total flow rates (Q = sum of the Ar and Cl2 flow rates).

The phase change of the samples was analyzed using an X-ray diffraction system (XRD, Bruker D8 Advance). The analysis was conducted in the 2θ range of 10–80° with a step size of 0.0104° and measurement time of 0.15 s during each step.

## 3. Results and discussion

The ΔG values of the Li2ZrO3 chlorination reaction were derived using the HSC chemistry software. These results are shown in Fig. 1. The ΔG value represents the change in the chemical potential when the reaction proceeds, which is negative when the sum of the chemical potentials of the reaction products is smaller than that of the reactants. In other words, a negative ΔG indicates that the reaction is thermodynamically feasible. In Fig. 1, negative ΔG values were observed throughout the temperature range (300−1,000℃), suggesting that the Li2ZrO3 chlorination reaction is thermodynamically feasible. The volcano shape of the figure came from phase change of LiCl from a solid to a liquid at 610℃, which is the melting point of LiCl. The following equation, where ΔH and ΔS correspondingly represent changes in enthalpy and entropy, accounts for the volcano shape because the melting of LiCl leads to an increase in the ΔS value.

$Δ G = Δ H − T Δ S$
(9)

However, an experimental approach should be utilized in order to verify the actual operating temperature as the activation energy and rate of the reaction are not included in the ΔG values.

The effects of the reaction temperatures and times were also investigated, as shown in Fig. 2. In the figure, the term α, the conversion ratio, is noted, representing the ratio of Li2ZrO3 reacted with Cl2 over the input of Li2ZrO3. This value was calculated using the following equation,

$α = ( W f − W i ) / ( W i ) / ( ( 2 × M . W ⋅ LiCl + M . W ⋅ ZrO2 − M . W ⋅ Li2ZrO3 ) / M . W ⋅ Li2ZrO3 )$
(10)

where Wf and W i represent the final and initial weight of the samples, respectively, and M.W.LiCl, M.W.ZrO2, and M.W.Li2ZrO3 correspondingly represent the molecular weight of LiCl (= 42.39 g·mol–1), ZrO2 (=123.2 g·mol–1), and Li2ZrO3 (= 153.1 g·mol–1). Interestingly, no signs of the reaction were found at 300℃, while the reaction proceeded slightly at 400℃ (α = 0.117 after 8 h of reaction). It is clear here that the reaction temperature should be at least 400℃ to overcome the activation energy of the Li2ZrO3 chlorination reaction, although the reaction is very slow at 400℃. In addition, this outcome shows why the experimental approach should be used in conjunction with thermodynamic calculations. With an increase in the reaction temperature to 450 and 500℃, a profound increase in α was observed. The reaction was found to be complete after 4 h at 500℃. A further increase in the reaction temperature to 600℃ brought a significant increase in the value of α, especially in the region of α ≤ 0.5. It is obvious from this result that the reaction temperature is a key parameter which determines the reaction rate and maximum value of α, especially in the temperature range of 400−600℃. Reproducibility of the experiments was verified by repeating identical experiments three times at 600℃ for 1 h under a 98 mL∙min–1 Ar + 2 mL∙min–1 Cl2 flow. These results are shown the error bar in Fig. 2, where the resulting α value was 0.508 ± 0.025. This outcome proves the acceptable reproducibility of the experiments conducted in this work.

Activation energy of the Li2ZrO3 chlorination reaction was derived using the data of Fig. 2. In a gas-solid reaction, the reaction rate can be expressed using the following equation,

$R = d α d t = k ( T ) F ( p Cl 2 ) G ( α )$
(11)

where k(T), F(pCl2), and G(α) represent the effects of reaction temperature, chlorine partial pressure, and morphological changes, respectively. Applying the Arrhenius equation in k(T) and integration of Eq. (11) results in the following equation,

$− ln ( t ) = C ( α ) − E a R g 1 T$
(12)

where C(α) represents combination of F(pCl2) and G(α) at a constant pCl2, Ea is an activation energy, and Rg is the gas constant (8.314 J·mol–1·K–1). Here, the Ea value can be derived from the slope of –ln(t) versus 1/T plot for a given α. The experimental results at α values of 0.2, 0.4, 0.6, and 0.8 are shown in Fig. 3 with linear fitting results. Here, linear interpolation was applied to the α and t values. It should be noted that the results at 600℃ were not included in the linear fitting calculations because of significant discrepancy in the trend. The activation energy calculated from the results at 450 and 500℃ was 102 ± 2 kJ·mol–1·K–1. These results also propose that the reaction regime is changing between 500 and 600℃.

Phase changes in the samples prepared at 500℃ for 1.0 and 4.0 h were analyzed by XRD measurements, as shown in Fig. 4. After 1.0 h of the reaction (α = 0.2374), the XRD peaks could be assigned according to the three phases of Li2ZrO3 (PDF #01-070-8744), ZrO2 (PDF #01-078-0047), and LiCl (PDF #01-074-1972). Peaks of Li2ZrO3 were not observed after 4.0 h of the reaction (α =0.9922), as shown in Fig. 4(b), whereas peaks of LiCl-H2O (PDF #01-070-9971) were noted. Considering the hygroscopic characteristic of LiCl, the LiCl-H2O phase may have been generated during the sample handling process for the XRD measurements. These outcomes prove that the weight-based calculation of α was a reasonable approach for the experiments conducted at 500℃, assuming that the weight was measured as soon as the samples were exposed to air. In addition, the absence of unexpected reaction by-products was confirmed by XRD measurement results.

In a solid-gas reaction system, the reaction rate is controlled by either or both of mass transfer rate of gas, Cl2 in this work, and chemical reaction rate. Under a mass transfer rate controlled condition, an increase in the Q value leads to an increase in the reaction rate because the amount that is transferred to the surface of reactant, Li2ZrO3, affects the overall reaction rate. On the other hand, the reaction rate is independent of Q under the chemical reaction rate controlled condition. In order to identify the reaction mechanism of this work, the effect of Q at 500℃ was investigated by repeating experiments under various flow rates of 98 mL∙min–1 Ar + 2 mL∙min–1 Cl2 (Q = 100 mL∙min–1), 196 mL∙min–1 Ar + 4 mL∙min–1 Cl2 (Q = 200 mL∙min–1), and 294 mL∙min–1 Ar + 6 mL∙min–1 Cl2 (Q = 300 mL∙min–1) for various reaction times as shown in Fig. 5. Note that the ratio of Cl2 was kept constant at 2% of Q in order to eliminate the effect of Cl2 partial pressure. In the figure, an increase in the Q value leads to an increase in the reaction rate suggesting that the reaction is under the influence of Cl2 mass transfer rate at 500℃. It is interesting to observe the results with Q of 200 mL∙min–1, which exhibited similar values to those with 100 mL∙min–1 in the low ( < 0.2) and high ( > 0.9) α regions, and with 300 mL∙min–1 in the middle (0.5 < α < 0.85) region. Here, it is worth to note that the reaction time for high conversion ( > 90%) reduced less significantly, though it is clear that an increase in Q accelerates the reaction rate under the condition of this work.

A combined flow diagram of the ZrO2-assisted rinsing and Li2ZrO3 chlorination processes is displayed in Fig. 6 in comparison with the conventional salt distillation process. The concept of combining the ZrO2-assisted rinsing and chlorination processes involves the use of ZrO2-dispersed LiCl salt during the rinsing process. After a certain level of ZrO2 is converted into Li2ZrO3 by reacting with Li2O, bubbling chlorine gas through the rinsing salt can eliminate the need for a separate reactor for the chlorination process. When scaling up these processes, the bath size and the ZrO2 input of the rinsing process may be the key parameters determining the capacity of the rinsing bath and frequency of Li2ZrO3 chlorination. In addition, various aspects such as the process cost, operation time, and total process efficiency should be compared between the conventional salt distillation process and the ZrO2-assisted rinsing step combined with the chlorination process.

## 4. Conclusions

A chlorination reaction of Li2ZrO3 to recycle it as LiCl and ZrO2 via a ZrO2-assisted rinsing process was successfully demonstrated in various experiments. It was found that the reaction temperature is a key parameter of the reaction to achieve a high conversion ratio, suggesting an operating temperature of at least 450℃. The activation energy was estimated to be 102 ± 2 kJ·mol–1·K–1 at 450 and 500℃. The effect of Q on the α value at 500℃ indicated that the reaction rate of this study is under control of Cl2 mass transfer rate under the condition of this work. The outcomes of this work suggest that the chlorination technique can solve the problem of extra waste (Li2ZrO3) generation during the ZrO2-assisted rinsing process.

## Acknowledgements

This work was sponsored by the Nuclear R&D program of the Korean Ministry of Science and ICT (2017M2A8A 5015147 and 2017M2A8A5015077).

## Figures

ΔG values of the reaction between Li2ZrO3 and Cl2 (Eq. 8) at various temperatures calculated using the HSC chemistry software.

Experimental results obtained at various reaction temperatures and times with a flow rate of 98 mL∙min−1 Ar + 2 mL∙min−1 Cl2.

Plot of –ln(t) versus 1/T×103 for the calculation of activation energy at α values of 0.2, 0.4, 0.6, and 0.8 under a 98 mL∙min−1 Ar + 2 mL∙min−1 Cl2 flow.

XRD measurement results of Li2ZrO3 reacted at 500℃ for (a) 1.0 and (b) 4.0 h under a 98 mL∙min−1 Ar + 2 mL∙min−1 Cl2 flow.

Experimental results obtained at 500℃ for various Q values of 100 (= 98 mL∙min−1 Ar + 2 mL∙min−1 Cl2), 200 (= 196 mL∙min−1 Ar + 4 mL∙min−1 Cl2), and 300 mL∙min−1 (294 mL∙min−1 Ar + 6 mL∙min−1 Cl2).

Flow diagrams of (a) the conventional salt distillation process and (b) the ZrO2-assisted rinsing process combined with Li2ZrO3 chlorination.

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