Homogenization of Maritime Pine Wood Color by Alkaline Hydrogen Peroxide Treatment

: The color of maritime pine wood is a critical parameter for manufacturing high added value materials (wood ﬂooring or wood paneling for indoor applications). Actually, the color inho-mogeneity between heartwood (Hw) and sapwood (Sw) can lead to a depreciation of the wood value and, therefore, to ﬁnancial losses for wood products companies. In this article, the development of a color homogenization process based on alkaline hydrogen peroxide chemistry was studied. Maritime pine heartwood and sapwood powders were used to facilitate the chemical characterizations and colorimetric analyses by the CIEL*a*b* system. Brighter materials were obtained after the treatment by reducing signiﬁcantly the color difference. The chemical modifications of wood surface were characterized by infrared spectroscopy analyses. The color evolution of the material overtime was also studied thanks to an accelerated ageing under UV irradiation. It was demonstrated that even if a color reversion occurred by oxidation, the color remained homogeneous between heartwood and sapwood.


Introduction
Maritime pine is one of the most common softwood found in South West of France, covering one million hectares of the country forestry area [1]. It is mainly used for its wood, which possesses good mechanical properties; high elastic modulus (8800 MPa), low density (550 to 750 kg·m −3 ), and long fibers (2.5 to 5 mm versus 0.8 to 2.5 mm for hardwood) [2]. These characteristics make maritime pine suitable for packaging purposes (ex: wood pallets) or engineered wood products for indoor and decorative applications (wood flooring, wood paneling). Nevertheless, due to the consumers' feedbacks and specifications, industries identified a major issue: the color difference between heartwood and sapwood. This issue is particularly present in the case of decorative wood where the visual aspect is an important parameter to control.
Wood color is mainly attributed to lignin [3,4] and extractives. Lignin is a polyphenolic macromolecule biosynthesized from coumaryl alcohol, coniferyl alcohol, and synapyl alcohol. Quinone and coniferaldehyde units are known to have the greatest impact on color [5][6][7]. The latter, which are present only in a low amount in lignin (less than 4%), [6] absorb light radiations between 300 and 450 nm (with a maximal absorption at 350 nm) [8,9]. Quinones are produced either during the biosynthesis of lignin or by oxidation of phenolic structures. The well-known structures are ortho-quinone (λ max = 420 nm) and para-quinone (λ max = 373 nm).
Extractives are secondary metabolites. They confer different properties to the wood such as protective effects against insects, mold, and also wood destructive fungi, wood fragrance (terpenes), and color. Phenolic extractives, which have several chromophoric moieties, play a major role on this parameter. According to heartwood type, the synthesis and evolution of those extractives might be different [10]: for Pinus-type heartwood, phenolic precursors are synthetized in sapwood and then modified in the transition zone.
It was suggested in several studies that those low molecular weight phenolic molecules present in the transition zone evolved into more complex structures within heartwood. This was observed for hardwood [11][12][13][14] as well as softwood [15][16][17][18][19][20]. Even if those complex materials are present in low amount, they can highly influence wood color as shown in the study of Johansson et al. on red cedar wood extractives. An insoluble fraction, with a molar mass between 1000 and 10,000 g·mol −1 , was recovered after extraction and fractionation in methyl t-butyl ether (MTBE), corresponding to only one third of dry matter but being responsible for 70% of the color of the sample.
Because of these chemical composition differences, maritime pine heartwood has a brown-reddish color while sapwood is yellow.
In addition to homogenization, lighter shades are now more and more appreciated by customers. Treatments based on paper processes chemistry make then suitable candidates for the modification of wood color. Oxidative compounds like oxygen, ozone, or hydrogen peroxide are preferred and commonly employed in Totally Chlorine Free (TCF) bleaching sequences [21][22][23][24][25].
Hydrogen peroxide (H 2 O 2 ) is usually found in aqueous solutions and, therefore, is more easily handled than the two other oxidants. Quite ineffective when used alone, an alkali as sodium hydroxide (NaOH) is added to produce perhydroxyl anions (HOO -), which are better oxidizing agents than the native peroxide [26,27]. H 2 O 2 stability in solution can be improved by adding metal chelatants or stabilizers like magnesium salts (magnesium sulfate, MgSO 4 ) or silicates (sodium metasilicate, Na 2 SiO 3 ) [28,29]. The reaction between alkaline hydrogen peroxide and wood can be influenced by several parameters: H 2 O 2 and alkali concentrations, pH, temperature, and treatment duration. Hydrogen peroxide treatment has been used since the 1930s to successfully modify wood color but very few studies [30,31] were made on the influence of the process on the color homogenization between heartwood and sapwood.
Herein, we report in the present study the results of wood color homogenization by alkaline hydrogen peroxide treatments. The experiments were done on wood powders to facilitate the chemical characterizations before and after the treatment. Soxhlet extractions were carried out to observe the effect of the bleaching on the wood extractives' structure. Heartwood (Hw) and sapwood (Sw) were treated separately with a solution composed of hydrogen peroxide, sodium hydroxide, and sodium metasilicate. Color changes were studied with colorimetric analyses and chemical evolutions were observed with infrared analyses. The impacts on wood color of the variation of NaOH concentration or the substitution of NaOH by another alkali source were also studied. Finally, ageing experiments under UV irradiation were carried out to examine the behavior of the treated powders overtime.

Wood Samples
A 60-70 years old maritime pine log with a high red heartwood content was selected in a local sawmill (Gascogne Bois sawmill).

Hydrogen Peroxyde Treatment
For all the experiments, the wood/solvent mass ratio was 1/20. The bleaching solution was composed of H 2 O 2 (4% v ), alkali (NaOH or Mg(OH) 2 ; 1% w ), and Na 2 SiO 3 (0.4% w ). Alkali and Na 2 SiO 3 were first solubilized in water in a round bottom flask. The latter was put in an oil bath and the temperature was set at 60 ± 1 • C. Then hydrogen peroxyde was added and finally heartwood or sapwood powders were put into the solution under vigorous stirring. After 1 h, the powder was collected, washed with distilled water, filtered, and finally dried in an oven at 50 • C under vacuum for 12 h. The powder was then stored at room temperature and relative air humidity and kept away from light to prevent any color change.

Hydrogen Peroxide Concentration Monitoring
A spectroscopic method based on Baga et al.'s work was developed [33]. A calibration curve was established first to determine the concentration range for which Beer-Lambert's law was respected (absorbance below 1). During the reaction, a 2.5 µL aliquot was collected from the batch and put into a 25 mL-volumetric flask and then filled up with water. Then, 10 µL of this solution were taken out, added to a 10 mL-volumetric flask as 1 mL of a copper (II) sulfate aqueous solution at 0.01 mol.L −1 and 1 mL DMP alcoholic solution. A [2Cu(DMP) 2+ ] complex was formed with a maximal absorbance at 454 nm. The Equation (1), following, gives the correlation between hydrogen peroxide concentration and the absorbance:

Attenuated Total Reflectance Spectroscopy (ATR)
ATR analyses were carried out on Bruker Vertex 70 device fitted with a Pike GladiATR plate. Resolution was set at 4 cm −1 and 64 scans were accumulated between 400 and 4000 cm −1 for each experiment.

Soxhlet Extraction
Powders were extracted using a Soxhlet device and acetone as a solvent. Oil bath temperature was set at 75 ± 1 • C and the extraction was carried out for 8 h with a rate of 3-6 siphoning per hour. Extracts were then concentrated and let under dynamic vacuum during a night to remove the last solvent traces. Untreated and peroxide treated powders were extracted to compare the evolution of extractive composition.

Colorimetric Analyses
Wood powders color evolution was monitored by a Nix Pro Color 2 colorimeter. The device source was composed of three High-CRI LEDs and the illuminant D50 was chosen. Observation angle was set at 2 • and optical aperture was fixed at 15 mm. Wood powders were pressed with a laboratory pellet press (Specac, 12.5 MPa applied for 5 min) to form 50 mm diameter discs. Five measurements were performed on the smoothest surface. CIEL*a*b* 1976 system was used for the study and the value of the three colorimetric parameters L* (lightness), a* (green-red coordinate) and b* (blue-yellow coordinate) could be determined for each sample.
The color difference between heartwood (Hw) and sapwood (Sw) is given by Equation (2): It was aimed in this study to get ∆E Sw/Hw values as low as possible, so that the color differences are no longer discernible (ideally ∆E Sw/Hw ≤ 1 with the colorimetric system used).

UV Irradiation Ageing
Wood discs were irradiated with UV light produced by four black light tubes (TFWN18-Mazdafluor). Irradiance was determined with a CCD Thorlab spectrometer I 365nm = 0.45 mW.cm −1 . The temperature was kept under 40 • C by an air flux. Treated and untreated wood were irradiated for 69 days, and the color was monitored (colorimetric analyses as described in Section 2.6) at regular intervals (measurements every seven days from day 0 to day 49, last measurement was done on day 69).

Effect on Wood Extractives
The modifications were observed briefly after the beginning of the peroxide treatment: the color of wood fades and become brighter and the solution becomes yellowish due to the solubilization of extractives. Soxhlet extractions were carried out to observe the influence of the treatment on extractive content. For untreated wood, the yields recovered after extraction were 15.5% and 7.8% for heartwood and sapwood, respectively. Those values decrease drastically for the treated samples (1% for Hw and 0.5% for Sw) supporting the behavior of extractives and showing that their solubilization could have an impact on the coloration of the solution. The only compounds that remain on wood after bleaching are supposed to be fatty acids or sterols derivatives due to their hydrophobicity and low reactivity towards peroxide treatment [34,35].
Chemicals changes were assessed by ATR analyses, Figure 1 shows the differences between untreated and modified heartwood: bands disappearance between 1720-1740 cm −1 ( Figure 1a) and between 1690-1700 cm −1 (Figure 1b) corresponding to carbonyl groups that could be associated to various substances, including fatty acids and resins. The same behavior was observed for sapwood powders.

Color Changes
Color changes were characterized by colorimetric measurements (Figure 2). For both heartwood and sapwood, a decrease of a* and b* values as well as an increase of L* value have been observed after the treatment. The success of the treatment was highlighted by the determination of ∆E Sw/Hw values: 6.2 before bleaching versus 1.7 after bleaching.
Heartwood and sapwood discs before and after hydrogen peroxide treatment are observed in Figure 3.

Color Changes
Color changes were characterized by colorimetric measurements (Figure 2). Fo heartwood and sapwood, a decrease of a* and b* values as well as an increase of L* have been observed after the treatment. The success of the treatment was highlight the determination of ΔESw/Hw values: 6.2 before bleaching versus 1.7 after bleaching. Heartwood and sapwood discs before and after hydrogen peroxide treatment are observed in Figure 3.
.   Heartwood and sapwood discs before and after hydrogen peroxide treatment are observed in Figure 3.  Color homogenization was attributed to two parameters: • Extractives solubilization and modification: extractives have a high impact on wood color, especially heartwood's one and the redness (a* parameter) is correlated with these secondary metabolites. • The alkaline environment during the treatment promotes the formation of carboxylates and phenolates, which are more soluble than native extractives, which leads to the decrease of a* values [35,36]. • Chemical modifications of unextractable wood chromophores (lignin and high molecular weight compounds formed from extractives): As mentioned previously, coniferaldehyde units and quinones have a major influence on wood color even if they are present in a low amount. • Perhydroxyl anions can reacts with these structures [27,37]: Coniferaldehyde units are subjected to addition in α position that lead to an oxirane formation after rearrangement. After a final HOOadding, methanoate anion as well as vanillin-type derivative are formed as shown in Figure 4a. The addition of HOOleads to ringopening reactions for orthoquinone derivatives and to ring-degradation for paraquinone units (Figure 4c). Finally, colorless compounds called hydroquinones can be formed (Figure 4b) [38]. As determined in Forsskahl et al.'s study [39], methoxy-pbenzoquinone (λ max = 355 nm) is transformed into methoxy-p-benzohydroquinone ((λ max = 290 nm).

Influence of NaOH Concentration Variation and Treatment Duration/H2O2 Consumption
Hydrogen peroxide treatment is highly sensitive to the sodium hydroxide concentration. When a large amount of alkali is introduced in the solution, H2O2 may be totally consumed, which may generate secondary reactions that will induce alkaline darkening

Influence of NaOH Concentration Variation and Treatment Duration/H 2 O 2 Consumption
Hydrogen peroxide treatment is highly sensitive to the sodium hydroxide concentration. When a large amount of alkali is introduced in the solution, H 2 O 2 may be totally consumed, which may generate secondary reactions that will induce alkaline darkening [41,42].
The impact of NaOH concentration was studied by monitoring the color difference between heartwood and sapwood.
In addition to the previous experiments with 1% NaOH, three new conditions (Table 1): low amount of NaOH (3), H 2 O 2 and NaOH in equimolar quantity (5), large excess of NaOH (6) were performed and the results were compared to untreated (1), control (2, water treated), and 1% NaOH (4). Treated and untreated heartwood and sapwood samples are observed in Figure 5, and Figure 6 shows the evolution of L*, a*, and b* values versus the NaOH concentration in solution: • L* parameter (Figure 6a): there is no significative difference between the experiments for heartwood. For sapwood on the other hand, L* values decrease with the increase of NaOH concentration. • a* parameter (Figure 6b): For heartwood as for sapwood, all values decrease compared to untreated powders but with no significative influence of NaOH concentration. The lowest difference is obtained for 1%w. • b* parameter: Values are strongly dependent on NaOH percentage shown in Figure 6c and keep increasing with the concentration, especially for heartwood samples. Consequently, wood powders treated with a solution containing 10% NaOH look more yellow than the others as shown in Figure 6.  Treated and untreated heartwood and sapwood samples are observed in Figure 5, and Figure 6 shows the evolution of L*, a*, and b* values versus the NaOH concentration in solution: • L* parameter (Figure 6a): there is no significative difference between the experiments for heartwood. For sapwood on the other hand, L* values decrease with the increase of NaOH concentration. • a* parameter (Figure 6b): For heartwood as for sapwood, all values decrease compared to untreated powders but with no significative influence of NaOH concentration. The lowest difference is obtained for 1%w. • b* parameter: Values are strongly dependent on NaOH percentage shown in Figure  6c and keep increasing with the concentration, especially for heartwood samples. Consequently, wood powders treated with a solution containing 10% NaOH look more yellow than the others as shown in Figure 6.  The best homogenization is obtained for 1% NaOH as shown in Table 2. For lower NaOH concentration, ∆E is high due to the brightness gap between heartwood and sapwood. For higher NaOH quantity, b* parameter has the greatest impact on ∆E as ∆b* values increase with the concentration.   In order to avoid alkaline darkening, H 2 O 2 total consumption should be prevented. The consumption of hydrogen peroxide was monitored for the treatment with 1% NaOH since this percentage leads to the best value of ∆E and have been reported in Figure 7a. H 2 O 2 concentration decreases until 60 min of treatment and then remains stable. The oxidant is not totally consumed, which may prevent secondary reactions between hydroxyl anions and lignin. The correlation between H 2 O 2 consumption and ∆E evolution (Figure 7b) confirms that ∆E does not change anymore when oxidant concentration reaches its minimum value.
The best homogenization is obtained for 1% NaOH as shown in Table 2. For lower NaOH concentration, ΔE is high due to the brightness gap between heartwood and sapwood. For higher NaOH quantity, b* parameter has the greatest impact on ΔE as Δb* values increase with the concentration. In order to avoid alkaline darkening, H2O2 total consumption should be prevented. The consumption of hydrogen peroxide was monitored for the treatment with 1% NaOH since this percentage leads to the best value of ΔE and have been reported in Figure 7a. H2O2 concentration decreases until 60 min of treatment and then remains stable. The oxidant is not totally consumed, which may prevent secondary reactions between hydroxyl anions and lignin. The correlation between H2O2 consumption and ΔE evolution ( Figure  7b) confirms that ΔE does not change anymore when oxidant concentration reaches its minimum value.

Influence of NaOH Substitution by Magnesium Hydroxide
As it was demonstrated previously, NaOH concentration in the solution is an important parameter to control. In order to get the best homogenization without yellowing reactions, NaOH was substituted with an alternative alkaline source: magnesium hydroxide (Mg(OH)2). This compound is already used in replacement of NaOH in paper mill processes [43][44][45][46][47]. Sodium hydroxide was partially or totally replaced by Mg(OH)2 as presented in Table 3.

Influence of NaOH Substitution by Magnesium Hydroxide
As it was demonstrated previously, NaOH concentration in the solution is an important parameter to control. In order to get the best homogenization without yellowing reactions, NaOH was substituted with an alternative alkaline source: magnesium hydroxide (Mg(OH) 2 ). This compound is already used in replacement of NaOH in paper mill processes [43][44][45][46][47]. Sodium hydroxide was partially or totally replaced by Mg(OH) 2 as presented in Table 3. The very low solubility of Mg(OH) 2 in water compared to NaOH (6.5 mg·L −1 vs. 1111 g·L −1 , respectively), triggers the hydroxide anion concentration since they are generated more slowly, which may limit yellowing reactions. Figure 8 shows the influence of the NaOH/Mg(OH) 2 ratio on colorimetric parameters values. The very low solubility of Mg(OH)2 in water compared to NaOH (6.5 mg·L g·L −1 , respectively), triggers the hydroxide anion concentration since they are more slowly, which may limit yellowing reactions. Figure 8 shows the influe NaOH/Mg(OH)2 ratio on colorimetric parameters values.

•
L* values increase when NaOH is partially replaced by Mg(OH) 2 . Nevertheless, there is a limit ratio beyond which a reversal trend is observed (0.5% NaOH/0.5% Mg(OH) 2 for heartwood, 0.25% NaOH/0.75% Mg(OH) 2 for sapwood). ∆L* values tend to increase with the substitution rate. • For a* parameter, a decrease is observed until the ratio 0.5% NaOH/0.5% Mg(OH) 2 , then values increase as for the gap between heartwood and sapwood. This trend may be easily explained by the difference of reactivity between the two alkalis. As mentioned before, the low solubility of Mg(OH) 2 in water allows a gradual release of hydroxide anion that will have an effect on the solution pH (value around 8-9 vs. 11-12 for NaOH solutions) [48]. Mg(OH )2 solubilizes in water to form first Mg(OH) + (pKs Mg(OH) 2 = 11.2) and then Mg 2+ and OH -(pKa (Mg 2+ /Mg(OH) + ) = 11.4 while pKa (Na+/NaOH) = 14.8 ) [49]. Due to the lower pKa of magnesium hydroxide, heartwood phenolic compounds should be less deprotonated and are still present. Consequently, a* values are higher when sodium hydroxide is fully substituted by magnesium hydroxide. As those extractives are not available in sapwood, a* values are less affected. • Finally b* values decrease with substitution rate and confirm that using Mg(OH) 2 could limit wood yellowing by preventing secondary reactions with hydroxide anions. Table 4 shows that the substitution of NaOH by Mg(OH) 2 leads to a color homogenization between heartwood and sapwood but not as effective as for a treatment using only NaOH. The 4% H 2 O 2 /0.5% NaOH/0.5% Mg(OH) 2 system shows color homogenization results as good as the 4% H 2 O 2 /1% NaOH. L* values are higher while b* values are lower when concentration in Mg(OH) 2 increases, consequently wood powders seems brighter than those treated with only NaOH.

UV Irradiation Ageing and Color Evolution
It is known that wood color is modified overtime [50,51] due to interactions with UV radiations in presence of dioxygen, which induce chemical processes by generating quinone derivatives [52][53][54][55]. These modifications depend on the wood species and on the weathering of the materials: in the case of outdoor applications, rain and humidity additionally induce a leaching phenomenon and a material destruction that is not observed in indoor applications. Finally, biodeterioration can also alter wood color.
As a consequence, heartwood and sapwood discs were irradiated in an UV irradiation chamber and color changes were monitored periodically for 70 days and compared to untreated samples. Only the irradiation of samples treated by a system 4% H 2 O 2 /1% NaOH was studied here. Figure 9 shows the evolution of colorimetric parameters values during the experiment. A fast color change is observed during the first week and until the 28th day, then a slower evolution takes place. For both samples, L* values decrease while a* and b* values increase and the evolution seems to be higher for the treated wood as shown in Tables 5 and 6. Chemical changes caused by UV irradiation ageing were observed by ATR analyses (Figure 10). The appearance of a band at 1710-1730 cm −1 is observed and attributed to the C=O bond of quinone-type fragments formed as described in the mechanism presented in  Chemical changes caused by UV irradiation ageing were observed by ATR analyses (Figure 10). The appearance of a band at 1710-1730 cm −1 is observed and attributed to the C=O bond of quinone-type fragments formed as described in the mechanism presented in Figure 11.
• UV radiations in presence of dioxygen induce a hydrogen abstraction on lignin hydroxyl groups. The addition of oxygen radical species (perhydroxyl, hydroxyl) or dioxygen followed by rearrangements generate quinones [40,56]. • Quinones are produced from hydroquinones formed from lignin during H 2 O 2 treatment [40].
Coatings 2021, 11, x FOR PEER REVIEW 16 • UV radiations in presence of dioxygen induce a hydrogen abstraction on lignin droxyl groups. The addition of oxygen radical species (perhydroxyl, hydroxy dioxygen followed by rearrangements generate quinones [40,56].

•
Quinones are produced from hydroquinones formed from lignin during H2O2 t ment [40].  ∆E values evolution was followed periodically during UV irradiation ageing; the results are presented in Figure 12. For untreated samples, an increase of the values is observed during the first week followed by a decrease. On the contrary, for bleached samples, a reverse trend occurs: a decrease during the first two weeks and then an increase. However, mean ∆E for bleached samples is lower than the untreated sample one showing that the color difference between treated heartwood and sapwood stay low after ageing. A comparison between untreated, bleached, and irradiated/bleached samples is shown in Figure 13: due to the color reversion induced by UV rays, irradiated samples appear more yellow and dark than the others; however, color between the two domains remains homogeneous. Figure 10. ATR traces of maritime pine heartwood (untreated and bleached) before and after UV irradiation ageing. Figure 11. Quinone derivatives formation under the influence of UV irradiation (a) and evolution of hydroquinone formed from H2O2 treatment into quinone (b) [40,56]. ΔE values evolution was followed periodically during UV irradiation ageing; the results are presented in Figure 12. For untreated samples, an increase of the values is observed during the first week followed by a decrease. On the contrary, for bleached samples, a reverse trend occurs: a decrease during the first two weeks and then an increase. However, mean ΔE for bleached samples is lower than the untreated sample one showing that the color difference between treated heartwood and sapwood stay low after ageing. A comparison between untreated, bleached, and irradiated/bleached samples is shown in Figure 13: due to the color reversion induced by UV rays, irradiated samples appear more yellow and dark than the others; however, color between the two domains remains homogeneous.

Conclusions
Maritime pine heartwood and sapwood colors were homogenized with paper bleaching processes based on alkaline hydrogen peroxide chemistry. First, H2O2/NaOH solution was used, and wood surface are lighter and brighter than the untreated ones. This behavior is attributed to the modification of chromophores (coniferaldehyde, quinones) and to the extraction of extractives by formation of anionic species due to the alkaline environment.
When the percentage of alkali is high, the peroxide may be totally consumed, which may promote secondary reactions between hydroxyl anions and wood and, thus, leads to

Conclusions
Maritime pine heartwood and sapwood colors were homogenized with paper bleaching processes based on alkaline hydrogen peroxide chemistry. First, H 2 O 2 /NaOH solution was used, and wood surface are lighter and brighter than the untreated ones. This behavior is attributed to the modification of chromophores (coniferaldehyde, quinones) and to the extraction of extractives by formation of anionic species due to the alkaline environment.
When the percentage of alkali is high, the peroxide may be totally consumed, which may promote secondary reactions between hydroxyl anions and wood and, thus, leads to alkali darkening. The best homogenization result is obtained for the 4% H 2 O 2 /1% NaOH system. The substitution of NaOH by Mg(OH) 2 leads to a decrease of b* parameter values and also to an increase of the L* values. Consequently, samples treated with this system appear brighter than the one bleached with a H 2 O 2 /NaOH solution.
Due to his poor solubility in water, the release of hydroxyl is progressive, which may prevent alkali darkening reactions. Best color homogenization was obtained for the 4% H 2 O 2 /0.5% NaOH/0.5% Mg(OH) 2 system. Finally, UV irradiation ageing experiments were carried out on both untreated and bleached samples. A color reversion was observed for all the samples irradiated and attributed to the formation of quinone derivatives. However, it was noted that the color between bleached heartwood and sapwood stayed homogeneous even after irradiation.
This preliminary study shows the effects of an alkaline hydrogen peroxide treatment on the color of maritime pine heartwood and sapwood powders. Facing these results, these experiments shall be applied on the treatment of veneer and solid wood considering the scale differences. Maritime pine wood is known to have a wide variability of extractives concentrations depending on the soil, the climate, or the position in the tree [57][58][59][60]. This parameter should be considered during the treatment and the composition of the hydrogen peroxide solution adapted to the material used.

Conflicts of Interest:
The authors declare no conflict of interest.