Preparation of PO43−-Intercalated Calcium–Aluminum Hydrotalcites via Coprecipitation Method and Its Flame-Retardant Effect on Bamboo Scrimber

To improve the flame retardancy of bamboo scrimber, flame-retardant CaAl-PO4-LDHs were synthesized via the coprecipitation method using PO43− as the anion of an intercalated calcium–aluminum hydrotalcite in this work. The fine CaAl-PO4-LDHs were characterized via X-ray diffraction (XRD), Fourier-transform infrared spectroscopy (FTIR), cold field scanning electron microscopy (SEM), energy-dispersive X-ray (EDX) and thermogravimetry (TG). Different concentrations (1% and 2%) of CaAl-PO4-LDHs were used as flame retardants for the bamboo scrimber, and the flame retardancy of the bamboo scrimber was characterized via cone calorimetry. The results showed that CaAl-PO4-LDHs with excellent structures were successfully synthesized via the coprecipitation method in 6 h and at 120 °C. Compared with the bamboo scrimber without the flame retardant treatment, the peak heat release rate (HRR) of the bamboo scrimber treated with 1% and 2% concentrations of flame-retardant CaAl-PO4-LDHs decreased by 16.62% and 34.46%, the time taken to reach the exothermic peak was delayed by 103 s and 204 s and the Time to Ignition (TTI) was increased by 30% and 40%, respectively. Furthermore, the residual carbon of the bamboo scrimber did not change significantly, increasing by 0.8% and 2.08%, respectively. CO production decreased by 18.87% and 26.42%, respectively, and CO2 production decreased by 11.11% and 14.46%, respectively. The combined results show that the CaAl-PO4-LDHs synthesized in this work significantly improved the flame retardancy of bamboo scrimber. This work exhibited the great potential of the CaAl-PO4-LDHs, which were successfully synthesized via the coprecipitation method and applied as a flame retardant to improve the fire safety of bamboo scrimber.


Introduction
Bamboo scrimber is a new type of composite bamboo lumber, which is made from bamboo culms crushed into loose reticular fibrous bundles [1,2]. In recent years, bamboo scrimber has been widely used in construction and decoration materials due to its excellent mechanical properties and environmental friendliness [3]. However, bamboo scrimber is a flammable material with significant fire hazards due to the raw material's nature, which greatly limits its industrial application [4,5]. Therefore, conducting flame retardancy research on bamboo scrimber is of great significance.
In recent years, layered double hydroxides (LDHs) have been emerging as a new generation of environmentally friendly flame-retardant material, which is a new type of layered inorganic functional material made of a positively charged main layer and interlayer region containing charge-compensating anions [6,7]. Its general formula is M 3+ +M 2+ . The most common M 2+ : M 3+ ratios are 2:1 and 3:1 [8][9][10]. LDHs can be prepared via coprecipitation at an adjusted pH followed by the hydrothermal aging of the precipitate [11]. LDHs have been shown to offer excellent flame retardancy and smoke suppression properties due to their unique chemical composition and layered structure. Furthermore, the layer surface of flame-retardant LDHs is abundant in hydroxyl groups, which can form hydrogen bonds with the numerous hydroxyl groups in bamboo, enabling LDHs to stably bind to the bamboo and preventing leaching [12]. Therefore, flame-retardant LDHs can be a useful solution to the current problem of easy leaching in flame retardants.
More importantly, numerous studies have demonstrated that the introduction of new organic anions or functional flame-retardant anions in the interlayer can effectively improve the flame-retardant efficiency of LDHs. For example, Liu et al. [13] investigated the synthesis of sodium dodecylbenzene sulfonate (SDBS)-intercalated aluminum hydroxide via coprecipitation and ion exchange. Xu et al. [14] prepared the triazine-sulphonate pillared layered double hydroxides (LDH-NS). The research results indicate that the thermal stability of LDHs prepared via intercalation is significantly improved. Currently, phosphorusbased flame retardants are non-toxic and low-smoke and are an important part of bamboo flame-retardant research [15,16]. PO 4 3− containing flame retardants will produce PO• free radicals during the combustion process, which can bind H• or HO• in the flame and air, so as to achieve a flame-retardant effect [17]. However, the significant disadvantages of phosphorus-based flame retardants are the complex preparation process, easy leaching and low compatibility. Thus, based on the anion-exchangeable characteristics of LDHs [18], PO 4 3− with flame-retardant effects can be intercalated into the interlayer of LDHs to enhance the flame retardancy.
In addition, the cations on the LDH layer can be replaced by other cations; for example, Damindarova et al. [19] prepared tin-aluminum hydrotalcites and Zhang [20] prepared zinc-aluminum hydrotalcites. There are abundant and inexpensive reserves of calcium and phosphorus in the world, and among available works, one can rarely find a comprehensive report on the flame retardancy of calcium-aluminum hydrotalcites. Thus, Ca 2+ with flame retardancy can be chosen as a substitute for divalent cations on the LDH layer to prepare flame-retardant calcium-aluminum hydrotalcites with high thermal stability.
In this work, PO 4 3− was selected for the intercalation modification of LDHs containing Ca and Al on the layer. CaAl-PO 4 -LDHs were synthesized via the coprecipitation method under alkaline conditions and applied to bamboo scrimber as flame retardants. The effects of different crystallization temperatures and times on the structure and properties of the synthesized CaAl-PO 4 -LDHs were investigated. Finally, bamboo scrimber was treated with different concentrations of CaAl-PO 4 -LDHs to further investigate the flame-retardant effect of CaAl-PO 4 -LDHs on bamboo scrimber. This work provided a certain theoretical basis for the application of flame-retardant PO 4 3− -intercalated calcium-aluminum hydrotalcites to bamboo scrimber.

XRD Analysis of CaAl-PO 4 -LDHs Synthesized via Different Processes
To explore the optimal processes for the preparation of CaAl-PO 4 -LDHs via coprecipitation, the CaAl-PO 4 -LDHs samples were synthesized and characterized at different crystallization temperatures (80 • C, 100 • C and 120 • C) and times (4 h, 6 h and 8 h). The effects of different crystallization temperatures and times on the structure and properties of CaAl-PO 4 -LDHs were investigated.
The XRD patterns of CaAl-PO 4 -LDHs synthesized after crystallization reactions are shown in Figure 1. The main characteristic peaks of CaAl-PO 4 -LDHs display sharp and intense (003), (006), (110) and (203) reflections corresponding to PDF#50-0652, which indicates that the prepared samples had a typical hydrotalcite lamellar structure [21]. The shifts in the diffraction peaks towards lower angles indicate that PO 4 3− was successfully inter- calated into the interlayer spacing of calcium-aluminum hydrotalcites [14]. Furthermore, as shown in Table 1, by Bragg's law (2dsinθ = nλ), the interlayer spacing (d 003 , d 006 and d 110 ) of CaAl-PO 4 -LDHs and PDF#50-0652 were calculated. The characteristic peaks of the samples synthesized at different crystallization temperatures and times were varied. The XRD spectrum shows that the characteristic peak of the sample (S 120-6 ) had the sharpest peak shape and the highest intensity. It has been concluded that a synthesis temperature of 120 • C and a duration of 6 h for crystallization are the optimal process parameters for the preparation of CaAl-PO 4 -LDHs.

Effects of Crystallisation Temperature on CaAl-PO4-LDHs
According to the XRD results, the effects of crystallization temperature (80 °C, 100 °C and 120 °C) at the optimum crystallization time (6 h) on hydrotalcite samples was

Effects of Crystallisation Temperature on CaAl-PO 4 -LDHs
According to the XRD results, the effects of crystallization temperature (80 • C, 100 • C and 120 • C) at the optimum crystallization time (6 h) on hydrotalcite samples was investigated. The structure of CaAl-PO 4 -LDHs samples synthesized via the co-precipitation method was characterized via FTIR, SEM, EDX and TG. Figure 2 shows that the positions of the absorption peaks of FTIR spectra of CaAl-PO 4 -LDHs synthesized at different crystallization temperatures are similar. The signals near 3470 cm −1 are related to the stretching vibration of the water molecules in the interlayer [22,23]. The absorption signal at 1628 cm −1 corresponds to the H-O-H bending vibration [14]. The characteristic absorption signals of the CO 3 2− group were observed at 1377 cm −1 and 792 cm −1 , which were caused by the adsorption of CO 2 by CaAl-PO 4 -LDHs after exposure to air at the end of synthesis [24]. The signals below 670 cm −1 were attributed to O-M-O bonds and M-O (where M is Ca or Al) bonds [25]. A telescopic vibrational signal of P-OH appeared at 1028 cm −1 , indicating that PO 4 3− was successfully inserted into the calcium-aluminum hydrotalcites [26]. PO4-LDHs synthesized at different crystallization temperatures are similar. The signals near 3470 cm −1 are related to the stretching vibration of the water molecules in the interlayer [22,23]. The absorption signal at 1628 cm −1 corresponds to the H-O-H bending vibration [14]. The characteristic absorption signals of the CO3 2− group were observed at 1377 cm −1 and 792 cm −1 , which were caused by the adsorption of CO2 by CaAl-PO4-LDHs after exposure to air at the end of synthesis [24]. The signals below 670 cm −1 were attributed to O-M-O bonds and M-O (where M is Ca or Al) bonds [25]. A telescopic vibrational signal of P-OH appeared at 1028 cm −1 , indicating that PO4 3− was successfully inserted into the calcium-aluminum hydrotalcites [26]. The method of EDX analysis enabled the indirect analysis of the successful insertion of PO4 3− anions into the interlayer [27], and the results are shown in Figure 3. The ratios of the relative contents of Ca and Al of the CaAl-PO4-LDHs samples were close to the theoretical value of 2.0, which indicated the successful synthesis of a typical layered hydrotalcite structure [28]. The content of elemental C in the samples synthesized at 100 °C was significantly higher due to the higher doping of carbonate in the samples. The C element was almost absent in S120-6, indicating the oxidation of this sample was less likely to produce CO3 2− . With the increase in the crystallization temperature, the P content first decreased and then increased. The highest elemental P content in the samples was reached at 120 °C. The results indicate the successful synthesis of CaAl-PO4-LDHs [29]. The method of EDX analysis enabled the indirect analysis of the successful insertion of PO 4 3− anions into the interlayer [27], and the results are shown in Figure 3. The ratios of the relative contents of Ca and Al of the CaAl-PO 4 -LDHs samples were close to the theoretical value of 2.0, which indicated the successful synthesis of a typical layered hydrotalcite structure [28]. The content of elemental C in the samples synthesized at 100 • C was significantly higher due to the higher doping of carbonate in the samples. The C element was almost absent in S 120-6 , indicating the oxidation of this sample was less likely to produce CO 3 2− . With the increase in the crystallization temperature, the P content first decreased and then increased. The highest elemental P content in the samples was reached at 120 • C. The results indicate the successful synthesis of CaAl-PO 4 -LDHs [29].  The microstructures of the CaAl-PO 4 -LDHs were revealed via SEM. As shown in Figure 4, the samples synthesized at different crystallization temperatures had corresponding lamellar structures. The sample with a crystallization temperature of 80 • C had an excellent lamellar structure, but the sample had poor layer order and a large size. Via crystallization at 100 • C, the resulting samples exhibited small particle sizes but with poor lamellar structures. The samples synthesized at a crystallization temperature of 120 • C had a uniform shape, uniform particle size and excellent lamellar structure. Therefore, 120 • C is a better crystallization temperature for CaAl-PO 4 -LDH samples.    The CaAl-PO 4 -LDH samples were investigated via TG-DTG in N 2 atmosphere, where the TG-DTG curves showed some differences. Figure 5 shows that the CaAl-PO 4 -LDH samples prepared at different crystallization temperatures all exhibited three thermal weight loss stages [30]. The first thermal weight loss stage (35-174 • C) is the loss of interlayer water molecules [31]. The S 120-6 showed the highest thermal weight loss (9.18%) compared to S 80-6 (6.66%) and S 100-6 (6.23%), indicating that the sample had the highest number of water molecules in the interlayer. In addition, small amounts of anions may be released in the first stage [32]. The second stage (181-342 • C) of thermal weight loss is the detachment of -OH from the surface of CaAl-PO 4 -LDHs [33]. The weight loss of the S 120-6 (11.75%) was lower than the other two samples (13.43% and 11.40%), which indicated that the layered structure was stable and numerous hydroxyl groups were not lost. The third thermal weight loss stage (450-629 • C) is a pyrolysis reaction via the anions in the interlayer [34]. In the third thermal weight loss phase, the S 120-6 showed the highest thermal weight loss (8.63%), showing the sample contains the most interlayer anions. Furthermore, the thermal weight loss temperature of the S 120-6 was slightly higher than that of the other two samples. Combined with the analysis of previous works, 120 • C is a better crystallization temperature for the preparation of CaAl-PO 4 -LDH samples via the coprecipitation method.

Effect of the Crystallisation Time on CaAl-PO 4 -LDHs
Based on the above analysis, the optimal crystallization temperature of 120 • C was determined, and then, the effects of different crystallization reaction times (4 h, 6 h and 8 h) on LDHs were investigated. The structures of CaAl-PO 4 -LDHs were investigated via FTIR, SEM, EDX and TG.
The FTIR spectra of the CaAl-PO 4 -LDHs samples synthesized at different crystallization times had similar positions of signals ( Figure 6). The signals near 3468 cm −1 were related to the hydroxyl stretching vibration in hydrotalcites. The signal at 1628 cm −1 was related to the bending vibration of the H-O-H [14]. The characteristic signals of CO 3 2− corresponded to 1380 cm −1 and 790 cm −1 [24]. The S 120-6 had almost no characteristic absorption band of CO 3 2− , indicating the sample was less oxidized. The signals at 1028 cm −1 were caused by the vibration of the PO 4 3− , showing PO 4 3− was successfully embedded in the calcium-aluminum hydrotalcites [26]. The signals below 670 cm −1 were caused by O-M-O bonds and M-O (where M is Ca or Al) bonds [25]. Figure 7 shows the EDX spectra of CaAl-PO 4 -LDHs samples prepared at different crystallization times. The values of the relative contents of Ca and Al elements of all CaAl-PO 4 -LDHs samples were close to the theoretical value of 2.0, indicating the successful synthesis of hydrotalcite structures [28]. With the increase in the crystallization time, the relative content of Ca and Al elements increased and then decreased, which revealed that the most LDHs were successfully synthesized when the crystallization time was 6 h. The high content of P elements in the samples synthesized at 6 h contributed to the higher content of PO 4 3− being successfully inserted into the interlayer of LDHs [29]. The microstructures of the CaAl-PO 4 -LDH samples prepared at different crystallization times were determined via SEM, and the results are shown in Figure 8. All the CaAl-PO 4 -LDH samples indicated layered structures, which confirmed that the samples had typical structures of hydrotalcites. At the crystallization temperature of 120 • C, the morphological changes in the samples were not obvious with the increase in the crystallization time. However, the samples with crystallization times of 8 h exhibited some tendency toward lamellar structures to aggregate. Figure 9 shows that the thermal weight loss pattern of the synthesized samples was consistent with the three stage thermal weight loss pattern of hydrotalcites [30,35]. The sample synthesized at 6 h (S 120-6 ) exhibited greater thermal weight loss (8.63%) than the others, S 120-4 (8.20%) and S 120-8 (7.78%), which indicates that the relative contents of -OH and PO 4 3− in these samples were higher than those in the other samples. In addition, the initial pyrolysis temperature of the sample prepared via crystallization for 6 h was slightly higher than the other samples. All the results were compared and analyzed to conclude that the better crystallization time for the synthesis of CaAl-PO 4 -LDHs via coprecipitation was 6 h. h) on LDHs were investigated. The structures of CaAl-PO4-LDHs were investigated via FTIR, SEM, EDX and TG.
The FTIR spectra of the CaAl-PO4-LDHs samples synthesized at different crystallization times had similar positions of signals ( Figure 6). The signals near 3468 cm −1 were related to the hydroxyl stretching vibration in hydrotalcites. The signal at 1628 cm −1 was related to the bending vibration of the H-O-H [14]. The characteristic signals of CO3 2− corresponded to 1380 cm −1 and 790 cm −1 [24]. The S120-6 had almost no characteristic absorption band of CO3 2− , indicating the sample was less oxidized. The signals at 1028 cm −1 were caused by the vibration of the PO4 3− , showing PO4 3− was successfully embedded in the calcium-aluminum hydrotalcites [26]. The signals below 670 cm −1 were caused by O-M-O bonds and M-O (where M is Ca or Al) bonds [25].   [28]. With the increase in the crystallization time, the relative content of Ca and Al elements increased and then decreased, which revealed that the most LDHs were successfully synthesized when the crystallization time was 6 h. The high content of P elements in the samples synthesized at 6 h contributed to the higher content of PO4 3− being successfully inserted into the interlayer of LDHs [29]. The microstructures of the CaAl-PO4-LDH samples prepared at different crystallization times were determined via SEM, and the results are shown in Figure 8. All the CaAl-PO4-LDH samples indicated layered structures, which confirmed that the samples had typical structures of hydrotalcites. At the crystallization temperature of 120 °C, the morphological changes in the samples were not obvious with the increase in the crystallization

Effect of Different Concentrations of Flame-Retardant CaAl-PO4-LDHs on Bamboo Scrimber
From conclusions from the previous work, CaAl-PO4-LDHs were prepared at the optimum crystallization temperature (120 °C) and time (6 h

Effect of Different Concentrations of Flame-Retardant CaAl-PO4-LDHs on Bamboo Scrimber
From conclusions from the previous work, CaAl-PO4-LDHs were prepared at the optimum crystallization temperature (120 °C) and time (6 h

Effect of Different Concentrations of Flame-Retardant CaAl-PO 4 -LDHs on Bamboo Scrimber
From conclusions from the previous work, CaAl-PO 4 -LDHs were prepared at the optimum crystallization temperature (120 • C) and time (6 h) to be used as flame retardants for bamboo scrimber. The heat release rate (HRR), Time to Ignition (TTI) and Mass of Residue (Mass) of the bamboo scrimber treated with different concentrations of impregnated flame retardant were investigated.
The heat release rate (HRR) can reflect the speed and magnitude of heat released from a fire source during the combustion process of a material [36]. As can be seen from Figure 10, the intensity of exothermic peaks of the bamboo scrimber treated with the S 120-6-1 and the bamboo scrimber treated with the S 120-6-2 were smaller than the non-flame-retardant-treated bamboo scrimber. The first exothermic peak started at 30 s, and it corresponded to a short flaming combustion process when the sample was ignited. The second exothermic peak corresponded to the combustion process at the second appearance of the higher flame [37]. The second exothermic peak intensities of the bamboo scrimber treated with the S 120-6-1 and the bamboo scrimber treated with the S 120-6-2 were 17.58% and 34.46% lower than that of the non-flame-retardant-treated bamboo scrimber, respectively. Secondly, the arrival time of the exothermic peak was delayed by 103 s and 204 s for the bamboo scrimber treated with the S 120-6-1 and the bamboo scrimber treated with the S 120-6-2 , respectively. The results indicate that the strong fire arrival time during combustion was delayed for the bamboo scrimber treated with the flame-retardant CaAl-PO 4 -LDHs, so the flame retardancy of bamboo scrimber was enhanced. The Time to Ignition (TTI) is the time required to produce continuous combustion on the surface of a sample due to thermal radiation [38]. A smaller TTI suggests higher combustibility. The TTIs of the control group and bamboo scrimber treated with different concentrations of impregnated flame-retardant CaAl-PO 4 -LDHs are shown in Table 2. Compared to the non-flame-retardant-treated bamboo scrimber, the TTIs of the bamboo scrimber treated with the S 120-6-1 and the bamboo scrimber treated with the S 120-6-2 were delayed by 30% and 40%, respectively, suggesting the heat resistance of the bamboo scrimber was improved. Furthermore, the bamboo scrimber treated with the S 120-6-2 exhibited a higher deferral rate of TTI, showing better flame retardancy.   Figure 11. The residual carbon rate indicated the final residual mass of the bamboo scrimber as a percentage of the initial mass. The residual carbon rates of the non-flame-retardant-treated bamboo scrimber, the bamboo scrimber treated with the S 120-6-1 and the bamboo scrimber treated with the S 120-6-2 were 22.24%, 23.12% and 24.32%, respectively. The results showed that CaAl-PO 4 -LDHs did not have a significant effect on the residual carbon rate of the bamboo scrimber and only slightly increased its residual carbon rate.  Figure 10. HRR of mass of non-flame-retardant-treated bamboo scrimber and flame-retardant bamboo scrimber. Materials produce many toxic gases during combustion, and the control of these gases is essential. As shown in Table 3, compared with non-flame-retardant-treated bamboo scrimber, the average CO production of bamboo scrimber treated with the S120-6-1 and bamboo scrimber treated with the S120-6-2 decreased by 18.87% and 26.42%, respectively, and the average arrival time of the maximum CO peak was delayed by 297 s and 253 s, respectively. In addition, the average CO2 production decreased by 11.11% and 14.46%, respectively, and the average arrival time of the maximum CO2 peak was delayed by 213 s and 268 s, respectively. These results indicate that CaAl-PO4-LDHs can suppress the Materials produce many toxic gases during combustion, and the control of these gases is essential. As shown in Table 3, compared with non-flame-retardant-treated bamboo scrimber, the average CO production of bamboo scrimber treated with the S 120-6-1 and bamboo scrimber treated with the S 120-6-2 decreased by 18.87% and 26.42%, respectively, and the average arrival time of the maximum CO peak was delayed by 297 s and 253 s, respectively. In addition, the average CO 2 production decreased by 11.11% and 14.46%, respectively, and the average arrival time of the maximum CO 2 peak was delayed by 213 s and 268 s, respectively. These results indicate that CaAl-PO 4 -LDHs can suppress the amount of CO and CO 2 production during bamboo combustion, and the delayed maximum peak arrival time can buy rescue time when a fire occurs. As shown in Figure 12, LDHs make bamboo produce char residue more easily, which can isolate O 2 and heat transfer between burning areas and the bottom of the carbon layer. During the combustion of CaAl-PO 4 -LDHs, hydroxyl groups on layers and interlaminar anions are released in the form of H 2 O and CO 2 , which can adsorb a lot of heat and reduce the concentration of combustion gas [39,40]. Thus, the heat release rate can be slowed down, and the ignition time of reconstituted bamboo can be delayed. Additionally, the final pyrolysis residue of CaAl-PO 4 -LDHs can also catalyze the formation of a more stable carbon layer and cover the surface of bamboo. The physical process of the char residue acts as a protective barrier, resulting in improved flame retardancy for bamboo [41]. So, the flame resistance of recombinant bamboo scrimber can be improved in this way.
Bamboo scrimber treated with the S120- As shown in Figure 12, LDHs make bamboo produce char residue more easily, which can isolate O2 and heat transfer between burning areas and the bottom of the carbon layer. During the combustion of CaAl-PO4-LDHs, hydroxyl groups on layers and interlaminar anions are released in the form of H2O and CO2, which can adsorb a lot of heat and reduce the concentration of combustion gas [39,40]. Thus, the heat release rate can be slowed down, and the ignition time of reconstituted bamboo can be delayed. Additionally, the final pyrolysis residue of CaAl-PO4-LDHs can also catalyze the formation of a more stable carbon layer and cover the surface of bamboo. The physical process of the char residue acts as a protective barrier, resulting in improved flame retardancy for bamboo [41]. So, the flame resistance of recombinant bamboo scrimber can be improved in this way.

Preparation of CaAl-PO4-LDHs via Coprecipitation
In this study, CaAl-PO4-LDHs were prepared via the coprecipitation method at 80 °C, 100 °C and 120 °C, and the crystallization times were 4 h, 6 h and 8 h. The pH value

Preparation of CaAl-PO 4 -LDHs via Coprecipitation
In this study, CaAl-PO 4 -LDHs were prepared via the coprecipitation method at 80 • C, 100 • C and 120 • C, and the crystallization times were 4 h, 6 h and 8 h. The pH value was kept at 10.0-11.00. In detail, we mixed Ca(NO 3 ) 2 ·4H 2 O and Al(NO 3 ) 3 ·9H 2 O with a M 2+ M 3+ molar cationic ratio of 2.0/1.0 (solution A) and prepared the solution of a strong base which was 1.5 mol/L NaOH. Then, solution A and NaOH solution were added into constant pressure funnels. A total of 41 g of Na 3 PO 4 was dispersed in 500 mL of deionized water in a 1000 mL three-necked flask before being stirred with a magnetic stirrer. After that, the reaction solution was put in 25 • C conditions for 16 h. Finally, the reaction solution was prepared via extraction, washing and drying to obtain CaAl-PO 4 -LDHs. Each group of experiments was repeated three times.

CaAl-PO 4 -LDH Flame-Retardant-Treated Bamboo Scrimber
The CaAl-PO 4 -LDH flame retardant was ultrasonically dispersed in an aqueous solution at 25 • C and prepared to suspensions of 1% and 2%. Then, the bamboo scrimber was dipped in the CaAl-PO 4 -LDH suspension and impregnated for 2 h at atmospheric pressure with simultaneous stirring [12]. After the impregnation, the suspended matter was removed from the surface of the bamboo scrimber samples with deionized water, and the bamboo scrimber samples were dried in an oven.

Characterization
X-ray diffraction (XRD) was carried out on an XRD-D2 produced by the German Brooke Company (Bremen, Germany). The scanning range was 5-70 • (2θ) and the scanning speed was 6 • /min. The samples were analyzed via FTIR spectroscopy using a Prestige-21 instument (Shimadzu Corporation, Shimane, Japan) with a scanning range of 400-4000 cm −1 . The potassium-bromide pellet method was used to determine the chemical composition of the samples prepared under different conditions (the samples were dried in an oven at 80 • C, and the dried samples were mixed with potassium bromide in a 1:100 ratio for grinding). The morphology and dispersion of samples prepared under different conditions were observed via the SU8010-type cold field emission SEM produced by Hitachi, Japan. The sample elements were investigated in combination with SEM to detect the relative content of Ca, Al and P elements in the sample. The thermogravimetric analysis (TGA) was measured using TA Q6000 (Naichi Instrument Manufacturing GmbH, Selb, Germany) at the heating rate of 20 • C/min under N 2 conditions with a temperature range of 35-800 • C and the flow rate of 40 mL/min. We determined the amount of charcoal residue in a sample by heating the sample to measure the weight change of the sample. Finally, the flame retardancy of the samples was tested using a conical calorimeter (CONE) manufactured by Nechi Instruments GmbH, Selb, Germany. According to the standard ISO 5660, the heat radiation power was 50 kW/m 2 and the sample size was 100 mm × 100 mm × 3 mm 3 . The results were obtained from the average of three replicates. All samples were wrapped in aluminum foil with no cover on the upper surface. The