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Effect of oxygen on produced hydrocarbons and hydrogen from CO2 reduction photocatalytic process
⁎Corresponding author. middlexyz@sina.com (Xinyong Zhao)
-
Received: ,
Accepted: ,
This article was originally published by Elsevier and was migrated to Scientific Scholar after the change of Publisher.
Abstract
A possible approach to addressing the challenges of energy scarcity and the effects of global warming through the decrease of greenhouse gases is the manufacture of hydrocarbons, particularly fuel from the photoreduction of CO2. Here, the determination of activity/selectivity of produced hydrocarbons, hydrogen, and oxygen in the gas phase was demonstrated in the absence and presence of O2 in an aqueous slurry on TiO2. The conversion increases with reaction time up to the first hour but then begins to become unchanged in the presence of oxygen, suggesting catalyst deactivation. In contrast, the reaction rate and CO2 conversion increased over 4 h when there was no oxygen, demonstrating that oxygen can be the cause of TiO2 deactivation. Intriguingly, light-induced O2 uptake rather than evolution was seen during optical oxygen detection investigations in photoreactions with a peak region of O2/CO2. H2 production is suppressed by the presence of oxygen. Additionally, the sudden increase in hydrogen generation when oxygen is absent demonstrated that oxygen consumption and hydrogen production are taking place at the reduction site. The availability of oxygen reduced hydrocarbon productivity and H2 production.
Keywords
CO2 reduction
Photocatalytic process
Oxygen
Hydrogen
Hydrocarbons
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1 Introduction
Anthropogenic activities cause an approximate global warming of ca. 1.0 °C beyond pre-industrial stages (IPCC, 2018). This global warming is anticipated to reach 1.5 °C from 2030 to 2052 if it keeps on enhancing at the present rate without the implementation of mitigation strategies (IPCC, 2018). This global warming is attributed to the increase in greenhouse gas emissions, which without simultaneous uptake by nature, has resulted in a rise in the concentration of these gases in the atmosphere (particularly CO2 which accounts for 60 % of global warming) (Khan & Tahir, 2019).
Fossil fuels have been a major cause of anthropogenic CO2 production over the years. In 2020, approximately 83.2 % of global energy demands were met by fossil fuels, although renewable energy sources reported 12.5 % of these demands (BP Energy outlook, 2021). The need for developing alternative sources of energy to cater to the increased energy needs of the world has thus become increasingly apparent, as global energy demands are projected to increase to approximately 30 TW by the year 2050 in a business-as-usual model (BP Energy, 2020; Lingampalli et al., 2017).
The linear molecule's strong thermodynamic stability as well as the kinetic inertness of CO2 lead to the low CO2 conversion efficiency in a reaction system (Li et al., 2021; Wei et al., 2018). In comparison to C–H (approximately 430 kJ mol−1) and C–C (about 336 kJ mol−1) bonds, the C⚌O bond in the CO2 molecule has a dissociation energy of roughly 750 kJ mol−1 (Li et al., 2021; Wei et al., 2018). Moreover, it has a relatively poor water solubility (about 30 mM at room temperature and pressure of 1 atm). Activation and conversion of CO2 are therefore extremely difficult (Li et al., 2021; Wei et al., 2018). In order to sort out these issues the photo-catalytic reduction of carbon dioxide to hydrocarbons may be a promising route to convert the greenhouse gas CO2 to useful products and limit the direct emission of CO2.
There are four main stages involved in the entire photocatalytic CO2 reduction reaction: (i) a semiconductor absorbing light to form electron-hole pairs, (ii) separating and transferring electron-hole pairs to the semiconductor surface, (iii) surface processes for oxidizing H2O, and (iv) surface reactions for reducing CO2 (Ran et al., 2018).
Among different kinds of semiconductors, TiO2 was used commonly for photocatalytic CO2 reduction in H2O because of low cost, non-toxicity, high surface area, activity, inertness, and resistance to photo-conversion (Kreft et al., 2020; Liu & Li, 2014) (Li et al., 2016; Xiong et al., 2015). For CO2 photo-reduction, mixed anatase/rutile is more effective than pure anatase or rutile (Li et al., 2008; Wang et al., 2012). It occurs as a result of the transfer that takes place between anatase and rutile as well as the effective charge separation caused by the establishment of a Schottky barrier (Scanlon et al., 2013; Tada et al., 2009). The results of the charge transfer mechanism, however, are not definitive.
It has proven possible to reduce CO2 by photocatalysis in both the liquid (slurry) and gas phases (flow and batch) (Kreft et al., 2020). Using a flow mode in the gas phase is fairly constrained because the product concentrations are much lower than in a batch reactor (Kreft et al., 2020). A slurry reactor's drawback in the liquid phase is the requirement for a large amount of water to be present (Kreft et al., 2020). The liquid phase is typically made up of water, which serves as a crucial reagent for CO2 but also inhibits CO2 conversion due to rival proton reduction (Kreft et al., 2020) (Reduction: 4H++4e−→2H2, Oxidation: 2H2O + 4 h+→O2 + 4H+).
Various semiconductors have been tested as oxidation photo-catalysts, but it is generally accepted that TiO2 is the most-often-used photo-catalyst (Augugliaro et al., 2008; Augugliaro & Palmisano, 2010; Blount & Falconer, 2002; Chen et al., 2010, 2013; Du et al., 2020; Ferry & Glaze, 1998; Higashimoto et al., 2014; Imamura et al., 2013; Kitano et al., 2014; Li et al., 2011, 2018; Ma et al., 2019; Ouidri & Khalaf, 2009; Ouyang et al., 2016; Palmisano et al., 2007; Pan et al., 2013; Pradhan et al., 2020; She et al., 2018; Song et al., 2019; Tamiolakis et al., 2015; Wang et al., 2015; Xie et al., 2014; Yurdakal et al., 2009, 2008; Zhang et al., 2017). The reasons for considering TiO2 as the most common photo-catalyst are reliability (Augugliaro & Palmisano, 2010; Imamura et al., 2013; Ouyang et al., 2016; She et al., 2018; Song et al., 2019; Tamiolakis et al., 2015; Xie et al., 2014; Yurdakal et al., 2009), low cost (Augugliaro & Palmisano, 2010; Imamura et al., 2013; Ouyang et al., 2016; She et al., 2018; Song et al., 2019; Tamiolakis et al., 2015; Xie et al., 2014; Yurdakal et al., 2009), low toxicity (Augugliaro & Palmisano, 2010; Imamura et al., 2013; Ouyang et al., 2016; She et al., 2018; Song et al., 2019; Tamiolakis et al., 2015; Xie et al., 2014; Yurdakal et al., 2009), photo-stability under irradiation (e.g., chemical and thermal stability) (Augugliaro & Palmisano, 2010; Imamura et al., 2013; Ouyang et al., 2016; She et al., 2018; Song et al., 2019; Tamiolakis et al., 2015; Xie et al., 2014; Yurdakal et al., 2009), activating by UV-light and also by solar radiation (Yurdakal et al., 2009), prompting of reaction under ambient temperature and pressure (Ouidri & Khalaf, 2009; Xie et al., 2014), easy availability (Xie et al., 2014), strong oxidation activity (Song et al., 2019), favorable optoelectronic properties (Leong et al., 2014), high-energy conversion efficiency(Song et al., 2019), high photoactivity (Schneider et al., 2014), large surface areas (Song et al., 2019) and low particle density (Song et al., 2019). The P25/TiO2 is a commercially available photocatalyst that has been used in many processes.
No studies have been found to quantify or even detect oxygen using P25/TiO2. Dou et al. investigated the surface reconstruction of ZnO using facile light irradiation and it led to the promotion of CO2RR to CH4 kinetic as well as O2 evolution reaction, but it was caused inhibiting of the competing HER and CO production(Dou et al., 2021). Some studies quantify hydrogen but the oxygen was not measured there or was not investigated the effect of oxygen on produced hydrogen or produced hydrocarbons (Akhter et al., 2015; Fang et al., 2015; Galli et al., 2017; Li et al., 2016; Liu et al., 2015; Qamar et al., 2016; Reli et al., 2017; Tahir & Tahir, 2016; Xiong et al., 2015). N-TiO2/CuO catalyst showed the maximum formic acid generation, about 40 times higher than pure titanium dioxide. In contrast, N-TiO2/CeO2/CuO showed a higher H2 evolution, around ∼6 times higher than pure TiO2 (Ibarra-Rodriguez et al., 2022).
In this paper, the activity/selectivity of produced hydrocarbons, oxygen and hydrogen from gas phase measurements was determined in the presence of oxygen on P25/TiO2. A constant temperature of the reactor's contents is necessary while sampling the gas phase. The conversion increases with increasing reaction time up to the first hour of the reaction but then starts to flatten out using P25/TiO2 in the presence of oxygen suggesting catalyst deactivation. While both reaction rate and CO2 conversion were increasing over 4 h when there is no oxygen, showing deactivation of P25/TiO2 can be because of oxygen. Carbon deposition as the origin of catalyst deactivation was investigated using TGA and FTIR. Surprisingly, light-induced O2 uptake rather than evolution was seen during optical O2 detection investigations in photoreactions with a peak area of O2/CO2. A Significant amount of produced hydrogen belonged to the dark conditions as CO2 reduction is the photoinduced reaction and CO2 reduction is more competitive than water reduction. The presence of oxygen suppresses to production of H2. Also, when there is no oxygen, the hydrogen formation is increased abruptly which shows that oxygen consumption and hydrogen production are happening in the reduction site. Here, we show how the overall activity and selectivity of the reaction can change by oxygen.
2 Experimental
2.1 Catalyst characterization
The nanoparticles morphology in the synthesised photocatalyst was scanned by a transmission electron microscope machine (TEM) by a TECHNIA 200II operating at 200 kV. The BET surface area used in this test was defined by a Micromeritics Tri-Star II 3020 equipment (Vers. 2.00). X-ray diffraction (XRD) analysis was done by a Bruker laboratory X-ray diffractometer the phase composition of the catalysts was determined using this instrument. The analysis was run at 35 kV and 40 mA in the scan range of 20°–120° and a 0.043° interval The thermal analysis system made up of a controller, related software, and DSC-TGA was utilized to display mass loss and decomposition over a temperature range. The characteristic band of the organic compounds deposited on the catalyst during the reaction was identified using the Nicolette is10 FTIR spectrophotometer, an unique characterisation technique to the vibrational characterization of moieties within the sample. At a spectral resolution of 4 cm−1, 32 scans were conducted in the 500 cm−1 to 4000 cm−1 range.
2.2 Photocatalytic CO2 reduction
The photocatalytic selective oxidation of alcohols was performed in a 100 mL reactor. Typically, a mixture of photocatalyst (5 g/L) and 0.2 M sodium bicarbonate (NaHCO3, Merk, ACS reagent, ≥ 99.7 %) was dissolved in 100 mL of deionized water, and then injected into the reactor. In the absence of oxygen, nitrogen was sparged for 5 min to remove all available oxygen in the reactor. The suspension was sealed with a rubber stopper and aluminum crimp seal. The sealed contents were left for 24 h to ensure a uniform start time (vapor–liquid equilibrium (VLE)) for all conducted experimental runs. The suspension was photo-irradiated under magnetic stirring using a 350 W UV lamp (230 V ULTRA-VITALUX 3). The lamp was placed at a constant distance (100 mm) from the reactor. Fresh catalysts were used at different irradiation times (0.5–4 h) to have consistency and to have VLE in the reactor. The reactor was taken out of its enclosure and placed in the dark for 2 h to terminate the reaction and ensure uniformity in sample temperature (room temperature) before product analysis. After the reaction, the catalyst was recovered by washing with anhydrous ethanol and H2O and dried in an oven at 120 °C overnight to analyse spent catalysts. The organic products were analysed and identified by GC-FID. The chromatograph system is coupled with a Polyarc™ oxidizer-methanizer and with a flame ionization detector (FID) which allows for the analysis of inorganic molecules. GC-TCD was used to measure oxygen and hydrogen under oven temperature of 70 °C, reference flow of 15 mL min−1, makeup flow of 3 mL min−1, carrier and reference gas of argon.
3 Result and discussion
3.1 Catalyst characterization
The refinement of the Powder X-ray diffraction (PXRD) pattern of the photocatalysts is given in Table 1. The crystal size of all catalysts was the same before and after the experiment. The P25/TiO2 had both anatase and rutile. A small decrease in rutile weight percentage and an increase of anatase in spent P25/TiO2 in the presence of oxygen have happened.
Parameters
Aeroxide® Degussa P25
Sample mass (g)
0.168
SBET BET Surface Area (m2/g)
51.3
Vpore Single point desorption (cm3 g−1)
0.159
dpore Desorption average pore diameter (Å)
124
The XRD patterns of the photocatalysts before and after experiments were done and were shown the same phases without any agglomeration after the experiment. Rutile and anatase phases were available before and after experiments.
Table 2 outlines the physio-chemical characteristics and a summary of the surface area and porosity measurements for each photo-catalyst. The physio-chemical characteristics of the P25/TiO2 in this study are comparable with previous studies (Nguyen & Wu, 2008; Wang et al., 2018). The P25/TiO2 photocatalyst surface area was 51.3 m2/g. Also, the pores volume and average pore diameter were 0.159 cm3 g−1 and 124 Å respectively.
Catalyst
Type of phase
Phase percentage (wt%)
Crystal size L (nm)
Fresh P25
Anatase
90.5
23.5
Rutile
9.5
51.7
Spent P25 in presence of oxygen
Anatase
89.5
25.3
Rutile
10.5
46.5
Spent P25 in absence of oxygen
Anatase
88.7
24.8
Rutile
11.2
50.7
The results of the “Thermogravimetric analysis (TGA)” are displayed in Fig. 1. The sample's mass in relation to temperature was normalized using the sample's starting weight. At a ramp rate of 10 °C/min, the temperature of the system was raised from the temperature of the room to about 1000 °C. The differential gravimetry (DTG) profile of the catalysts was obtained after more analysis by determining the derivative of the TGA profiles, as shown in Fig. 1. Using P25/TiO2, a normalized weight loss of ∼4 % was noted Following the P25/TiO2 experiment, there was significantly more weight loss in the presence of oxygen than without O2. The first pattern in the temperature between 25 °C and 200 °C indicates a mass reduction brought on by the release of H2O/organic solvents from the precursor as well as additive combinations utilized in the synthesis process. The second stage, which occurs at a temperature of 300–500 °C, represents the decomposition of the organic residue, which caused it to deactivate more readily in the presence of oxygen than in the absence of oxygen.Derivative (black) and weight loss (red) TGA profile of fresh (__) and spent P25 in the presence of oxygen (…) or in the absence of oxygen ( − − −) during experiment.
FTIR spectroscopy was used to analyse the lattice vibrational behaviour of the various samples, and the results are displayed in Fig. 2. On the spent catalysts, absorption bands that were absent on the new catalyst could now be seen. It had two distinguishing bands at 1400 cm−1 and 1500 cm−1. There were no changes in FTIR of spent P25/TiO2 either during the experiment in the absence of oxygen or in the presence of oxygen.FTIR spectra for the spent P25 in presence of oxygen (…), spent P25 in absent of oxygen (…), and fresh catalyst plotted as reference (___) in the range of 0–4500 cm−1.
A transmission electron microscope (TEM) was used to assess the morphology of the spent P25/TiO2 after using light for 4 hrs in the presence and absence of light (Fig. 3). Lighter coating in Fig. 3A can be seen surrounding the wasted catalyst particles than Fig. 3B. This thinner layer is a sign that amorphous material is present around the catalyst particles, maybe as a result of amorphous deposits on the catalyst. On the spent catalysts, some stringy, polymeric-looking material may be visible, which could indicate that the organics that were deposited there are polymeric in nature.TEM micrographs of A) spent P25 in absence of oxygen, B) spent P25 in presence of oxygen.
3.2 O2 photo-adsorption
Comparable to other TiO2 photocatalysis results from the past (Author et al., 2009; Kreft et al., 2019; Liu et al., 2013), as shown in Fig. 4, we were unable to identify O2 evolution in the gas phase using GC/TCD and just O2 consumption happened. Quantification of the missing amounts of oxygen in the gas phase revealed that the absence of this by-product in the CO2 reduction reaction could be caused by oxygen being consumed by TiO2 (Dilla et al., 2019). Also, the inhibitory impact of O2 on product formation in CO2 reduction demonstrates that TiO2 activity in this reaction depends on the consumption of this by-product (Dilla et al., 2019) or to be able to stop this by-product from being produced.Oxygen trend vs irradiation time using P25.
On a reduction site in the presence of oxygen, H2O, CO2 and O2 are being reduced. Without oxygen, hydrogen formation at the reduction site increases since there is one fewer competitor there. The electrons for CO2 and/or proton reduction are also provided by photooxidation of surface hydroxyl groups (Kreft et al., 2019). O2 adsorption decreased sharply up to 1 hr and then decreased gradually which can be because of the rate-limiting factor of low free surface area for adsorption after 2 hrs, as shown in Fig. 4. The peak area of O2/CO2 in the presence of oxygen was decreased from 5.4 to 1.3 but it is in the range of 0––0.06 in the absence of oxygen.
When there is oxygen, the oxygen photo-adsorption is prior to oxygen evolution. It was tried to degas the reactor from oxygen to check the oxygen production in the oxidation site from water, as shown in Fig. 4. Thus, the low oxygen evolution indicated just from 30 mins to 1 hr that either photogenerated O2 species stay adsorbed on the surface of synthesised photocatalyst and/or that another oxidation process is kinetically more favourable (Daskalaki et al., 2011). No studies have been found to detect or even quantify the oxygen using either TiO2. Xiong et. al., 2015 and 2017 compared the oxygen yields during the photocatalytic reaction and stoichiometric calculation based on the seen products which were a little less than the average production rate of oxygen, demonstrating that hydrogen, methane and CO were the major products of Pt2+Pt0/TiO2−3 and Pt-Cu2O/TiO2 (Xiong et al., 2015)(Xiong et al., 2017). In the other studies, the amount of O2 production on Pt4/PC-TiO2 (the weight ratios of Pt:TiO2 = 4:100) was more than the calculated theoretical value via the formation amounts for methane, hydrogen, and CO (Jiao et al., 2017). Therefore, other hydrocarbon products may be theoretically made but not recognised, which is because of the possibility that they may exist on the surface of the catalyst or wall of the reactor (Jiao et al., 2017). However, in this study, there was no oxygen evolution in the oxidation site to be able to compare with hydrocarbon production in the reduction site or there was oxygen evolution but was used in the reduction site for the reverse reaction.
3.3 Oxygen effect on CO and hydrocarbon formation
Reaction rate and CO2 conversion were incredibly higher when there was no oxygen using P25/TiO2 in both gas phase and gas–liquid equilibrium than when there was oxygen, Fig. 5. Both reaction rate and CO2 conversion were increasing because of producing CO and valuable hydrocarbons such as formic acid after 2 hrs when there is no oxygen, showing deactivation of P25/TiO2 can be because of oxygen. Also, it showed that oxygen is a competitor for CO2 reduction in the reduction site. The less hydrocarbon synthesis was due to the competition for charge carriers caused by the backward reaction of CO2 reduction in the presence of highly reactive oxygen species generated on catalysts. The CO2 conversation was increased from 0 to 0.5 % after 4 hrs in the presence of O2 while it was observed 3 % increase in the CO2 conversation in the absence of O2 after 4 hrs. Also, the reaction rate was deceased with time in the presence of O2 while it was seen a significant increase in the reaction rate in the absence of O2 in particular in the late 2 hrs.CO2 conversion and reaction rate vs irradiation time in gas phase.
Beller and his co-workers, 2019 tested CO production at different oxygen percentages in CO2 (0.1 %, 0.5 %, 5 % and 33 %) and found out whether CO would be available with or without oxygen and the highest amount of CO was investigated at 0.5 % and then 5 % (Kreft et al., 2019). Desorption of the oxygen species, which is difficult because TiO2 has an energy advantage over CO2 for adsorption on its surface, is a crucial component of photocatalytic efficacy. Hence, as reaction time increases, CO2 and O2 fight for the same adsorption sites on TiO2, which results in less CO2 adsorption and less product production (Kreft et al., 2020). In this experiment, there was no methane production either in the presence or absence of oxygen as fully degassing from oxygen was so difficult. When oxygen is present, there are certain reasons not to have methane or to only have a minimal amount of it employing catalysts. Experiments on photocatalytic CO2 reduction showed that methane synthesis is only possible in the absence of H2 and O2 (<5 ppm) (Dilla et al., 2019, Dilla et al., 2017). The absence of methane synthesis appears to be caused by the competition for charge carriers caused by H2 formation and the backward reaction of CO2 reduction caused by the presence of highly reactive oxygen species generated on catalysts (Dilla et al., 2019; Liu & Li, 2014). However, oxygen and hydrogen production during light absorption were minimal in this study (Figs. 4 and 6), and the availability of oxygen may have been the main factor.Hydrogen trend vs irradiation time using P25.
3.4 H2 formation
It has been established that the reduction of CO2 to hydrocarbons competes with the reduction of H2O to H2 as was mentioned in previous studies (Jiao et al., 2017). Moreover, when oxygen is absent, hydrogen formation increases suddenly (Fig. 6), demonstrating that oxygen consumption is also the same as hydrogen production and CO2 reduction takes place at the reduction site. The increase in H2 is linear in the absence of oxygen and it was increased from 0 to 0.7 after 4 hrs while the hydrogen production was reached 0.0057 after 4 hrs in in the presence of oxygen. Surprisingly, in this experiment, availability of oxygen (O2) decreased hydrocarbon productivity and H2 creation the opposite of the result of previous research that hydrocarbon was increased (Kreft et al., 2019). Beller and his colleagues studied hydrogen generation in 2019 using 6.3-Cu/TiO2-AG, TiO2-AG, and P25/TiO2 at various oxygen percentages in CO2 (0.1 %, 0.5 %, 5 %, and 33 %) and discovered that hydrogen would be negligible over 5 % O2/CO2 (Kreft et al., 2019).
On the one hand, some studies showed that the type of catalyst has an effect on CO2 reduction but not H2 production (Kreft et al., 2019; Liu et al., 2013; Singhal et al., 2016; Tseng et al., 2004). CO generation was three times higher when using 6.3 Cu/TiO2-AG (5.1 µmol gcat−1h−1) than it was when using pristine TiO2-AG (1.5 µmol gcat−1h−1); however, hydrogen evolution still predominated (430 vs 200 µmol gcat−1h−1) (Kreft et al., 2019). The activity toward CO increased significantly (10.9 µmol gcat−1h−1) when Cu loading was decreased to 0.3 wt%, but H2 production was only little impacted (490 µmol gcat−1h−1). More dispersion and smaller particles caused by less Cu on the surface avoid charge recombination, which encourages CO2 photo reduction but does not affect water reduction (Kreft et al., 2019; Liu et al., 2013; Singhal et al., 2016; Tseng et al., 2004). On the other hand, some research shows the catalyst will be effective in hydrogen production. Amorphous TiO2 can scavenge holes and greatly enhance charge carrier separation (Yu et al., 2016) and the defects in its structure can be advantageous (Ambrožová et al., 2018); increased hydrogen production from water splitting when using amorphous TiO2 and 0.5 wt% Cu/TiO2 (Ambrožová et al., 2018) than P25/TiO2.
4 Conclusion
The production of hydrocarbons from the photoreduction of CO2 is one potential strategy for resolving the issues of energy scarcity and the results of global warming by reducing greenhouse gases. Here, the gas phase measurements used to determine the activity/selectivity of generated hydrocarbons, hydrogen, and oxygen were shown in the presence and absence of oxygen in an aqueous slurry on P25/TiO2 to examine the impact of oxygen on their by-products. Up to the first hour of the reaction, the conversion goes up with reaction time, but after that, it starts to flatten out when employing spent P25 in presence of oxygen, which suggests catalyst deactivation. As evidence that oxygen can be the reason for P25/TiO2 deactivation, the reaction rate and CO2 conversion increased over the course of 4 h when there was no oxygen present. Intriguingly, during optical O2 detection investigations, light-induced O2 uptake rather than evolution was seen in photoreactions with a peak region of O2/CO2. The presence of oxygen inhibits the synthesis of H2. Furthermore, the fast rise in hydrogen generation in the absence of oxygen shows that oxygen consumption, CO2 reduction and hydrogen synthesis occur at the reduction site. Surprisingly, oxygen reduced H2 production and hydrocarbon output. The mechanism investigation, modification of photocatalyst structure, and investigation of affinity of adsorption material play a key role in enhancing CO2 photocatalytic reduction to produce more valuable hydrocarbons, oxygen, and hydrogen evolution. Furthermore, using XPS to address O spectra and clarification of oxygen vacancy level would be recommended in future studies.
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.
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