Efficient radon removal using fluorine-functionalized natural zeolite
Graphical abstract
Introduction
Radon is a radioactive inert gas classified as a Group I carcinogen radionuclide (IARC, 2012). The fission of naturally occurring radioactive materials such as 238U and 232Th in crustal rocks and minerals generates gaseous radionuclides, such as 222Rn, 219Rn, and 220Rn. Among these products, 222Rn, commonly known as Radon (Rn), is the most stable and possesses the longest half-life (3.82 days). Rn is colorless, tasteless, odorless, and heavier than air. Rn accumulates in the atmosphere where air circulation is insufficient because it is heavier than air, and it directly causes cancer by emitting alpha rays or decaying into daughter nuclides following inhalation (Samet, 1989). The actual risk posed by Rn is primarily ascribed to its daughter species, such as polonium, rather than to Rn itself.
Although Rn is an inert gas, it is also highly soluble in water (i.e., 230 cm3/L at 25 °C) at atmospheric pressure (Table 1) (Greenwood et al., 1997), and so can easily leak into the environment through groundwater. Rn, which is present in groundwater, affects the human body through two different routes of exposure, namely breathing exposure due to the volatilization of Rn in groundwater, and ingestion caused by drinking the water originating from Rn-contaminated groundwater Rn (Yu et al., 2001). Exposure to Rn through the respiratory pathway causes lung cancer, while drinking water contaminated with Rn exposes the gastrointestinal tract to Rn and its decay products.
Recently, the proportion of houses that take in groundwater and use drinking water and domestic water has increased, and so it is necessary to evaluate the health of the human body due to indoor contamination generated by the indoor volatilization of radon dissolved in the groundwater (Council, 1999). The globally averaged Rn concentration in groundwater is 4946 pCi/L (183 Bq/L) (NCRP, 1984). Since a Rn concentration of 10,000 pCi/L (370 Bq/L) in groundwater increases the indoor Rn concentration by 1 pCi/L (0.037 Bq/L), the recommended standard for the indoor Rn concentration in Korea has been set at 148 Bq/m3, while that for groundwater has been set at 148 Bq/L, as outlined in the Drinking Water Management Act of 2016. Unless appropriate action is taken to reduce the levels of Rn in groundwater, it will infiltrate into habitable areas and exhibit an adverse impact on the environment and society.
Due to their crystalline porous structures and flexible frameworks (suitable for controlled chemistry), zeolites have been widely employed in catalysis, sorption, and separation applications, among others (Davis, 2002; Breck et al., 1974; Guo et al., 2015; Yang et al., 1999; Cha et al., 2015; Fang et al., 2017). More specifically, zeolites have been applied for the sorption and removal of various hazardous species, including radionuclides, toxic metals, and gases, such as Rn (Yang et al., 2016; Ibrahim et al., 2010; Hedstrom et al., 2012). While many studies have been conducted into the removal of gaseous Rn, the extent of fundamental research into the removal of Rn from aqueous media remains limited.
However, recent reports have suggested that the leakage of Rn into the environment through groundwater is becoming a more serious concern, and research into its sorption and removal is gaining interest once again. The aim of this study is therefore to improve our understanding of the chemical factors that affect the Rn distribution in groundwater, and in particular, the presence of fluorine (F). Thus, we herein report a novel strategy for the sorption and efficient removal of Rn from groundwater (obtained from Daejeon, South Korea) using natural zeolite (NZ) and fluorine-functionalized natural zeolite (FFNZ) sorbents. Our findings can serve as a basis for the design and development of effective sorbents for Rn removal from natural groundwater in the future.
Section snippets
Materials
All reagents were of analytical grade and were used without further purification. NZ was obtained from Guryongpo, Pohang, South Korea, and ammonium fluoride (NH4F) was purchased from JUNSEI, Japan. Deionized water (Millipore water) having a specific resistivity of 18.2 MΩ cm at 25 °C was obtained from a commercial deionizer (Direct-Q® 5 UV Water Purification System).
Sample preparation
A high Rn content is found in uranium- and radium-rich granite, and in geological zones abundant in gneiss. In Daejeon, South
Crystalline structures and major elemental compositions of NZ and FFNZ
Fig. 1 shows the XRD patterns of NZ and FFNZ, whereby the intensities of the peaks corresponding to clinoptilolite-Ca and mordenite were relatively high (JCPDS file number: 25-1349). However, the peaks marked by the green arrows indicate the differences between the XRD patterns of the two solid samples, which confirm the presence of ammonium fluoride (NH4F), silicon fluoride hydrate (CaSiF·6H2O), and frankamenite (K3Na3Ca5(Si12O30)[F,(OH)]4·(H2O)) in the fluorinated sample. Based on the
Conclusions
In this study, we developed an improved understanding of Rn aqueous species in groundwater and evaluated the efficiency of Rn removal using modified zeolites. RDA was conducted using natural groundwater samples containing Rn, and it was found that the Rn content exhibited a positive correlation with the level of F present in groundwater. Therefore, the F species present in an aqueous phase may influence the retention of Rn in groundwater, enabling Rn to exist for a longer period than usual in
Declaration of competing 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.
Acknowledgements
This work was supported by supported by the Advanced Nuclear Environment Research Center (ANERC) from the National Research Foundation of Korea (NRF) (grant numbers NRF-2017M2B2B1072374 and NRF-2017M2B2B1072404).
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