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Electronic Supplementary Material (ESI) for Journal of Materials Chemistry A. This journal is The Royal Society of Chemistry Please do 17 not adjust margins Journal of Materials Chemistry A Supporting Information Thermal decomposition and recovery properties of ZnAl-CO 3 layered double hydroxide for anionic dye adsorption: Insight of the aggregative nucleation and growth mechanism of LDH memory effect. R. M. M. Santos a*, J. Tronto b, V. Briois c, C. V. Santilli a*. a. Instituto de Química da Universidade Estadual Paulista Júlio de Mesquita Filho (UNESP). Rua Prof. Francisco Degni, 55, 148-6, Araraquara-SP, Brazil. b. Instituto de Ciências Exatas e Tecnológicas, Universidade Federal de Viçosa, Campus de Rio Paranaíba. Rodovia BR 354, km 31, 3881-, Rio Paranaíba-MG, Brazil. c. Synchrotron SOLEIL, CNRS-UR1, L Orme des Merisiers, BP48, Saint-Aubin, 9119, Gif-sur Yvette, France. Multivariate Curve Resolution with Alternating Least Square fitting (MCR-ALS) Several recent works have proven the efficiency and power of the MCR-ALS procedure (Multivariate Curve Resolution - Alternating Least Squares) in the qualitative and quantitative investigation of time-resolved evolving XAS data recorded during solid-state reactions. 1-5 This statistical approach allows one to extract the components whose sum constitute the experimental spectra without introducing biases, such as resorting to hypotheses on the species involved during the reaction or using reference spectra that may not be appropriate. 6 A series of normalized XAS experimental spectra D, recorded upon reaction whose relative concentrations vary with time, temperature... is defined as a matrix D resulting from the combination of three matrices: C (concentration of the pure components); S (normalized XAS spectra of the pure components); and E (experimental uncertainties), following the matricial equation: D = C S T + E (where S T is the transposed matrix of S). The principle of the MCR-ALS analysis is to mathematically determine a likely set of concentrations C (varying along the series) and spectra S (constant along the series) which can explain the whole set of D, by iteration and least-squares minimization of the E matrix. For this scope, physically and chemically meaningful constraints on the C and S matrices are used in order to help the convergence of the multivariate curve resolution. In the present work, the matrix of concentrations C contains only positive values, each species is described with a single maximum on its concentration profile (unimodality) and the sum of the species concentrations is equal to 1% at any time of the reaction (closure relation). Additionally, the matrix S contains normalized XAS spectra with non-negative absorbance. The only information required by the MCR-ALS method to start the minimization is the number of pure components describing the matrix D to provide an initial guess either of the concentration matrix or of the component spectra matrix. This journal is The Royal Society of Chemistry xx J. Name., 13,, 1-3 1

Journal Name Singular Value Decomposition (SVD) method which describes D into orthogonal vectors is first used for the rank analysis of the C and S T matrices. A Scree plot, which displays the eigenvalues determined by SVD for each component arranged in descending order as a function of number of spectra in D, can be used for the estimation of the number of chemical components to include in the MCR-ALS minimization. The number of components to be retained using such Scree plot (Fig. S1) are those in the steep curve before the first point that starts the asymptotic line trend. Herein SVD analysis indicates that the variance of the D XAS experimental matrix recorded upon thermal decomposition of the pristine LDH is described considering only 3 components whereas only components are necessary for explaining the variance of the XAS data recorded upon recovery of the Calc-LDH in contact with aqueous or dye solutions. A detailed description of the SVD and MCR-ALS methods applied to XAS data can be found in references., 5 a) b) Fig. S1 Scree plot for determination of components to be retained in (a) LDH thermal decomposition and (b) LDH recovery in presence of dye. The MCR-ALS minimization on the Quick-XAS data presented herein was carried out using the MCR-ALS GUI. developed by Roma Tauler and his group on the Matlab platform. 7 An initial guess of the spectra in the ALS minimization was done using the SIMPLISMA (SIMPLe to use Interactive Self-modeling Mixture Analysis) method. 8 Fig. S displays the results of the minimization obtained for the thermal decomposition of the pristine LDH and for the recovery of the Calc-LDH in presence of dye. For the latter data set resolution (Fig. Sb), an additional constraint has been added with the addition of RT spectra of pristine LDH to the data set recorded during LDH recovery. This explains why the data with spectrum number higher than correspond to 1% of the component associated to the pristine LDH. J. Name., 1,, 1-3 This journal is The Royal Society of Chemistry xx

Journal Name a) b) Fig. S Results of the minimization obtained for: (a) the thermal decomposition of pristine LDH and (b) LDH recovery in presence of AB dye solution. This journal is The Royal Society of Chemistry xx J. Name., 13,, 1-3 3

Journal Name Normalised absorption (arb.units) 3 1 964 966 968 97 97 974 Energy (ev) nano-zno nano-znal O 4 Calc-LDH (45 C) dehydrated LDH (5 C) pristine LDH (RT) Fig. S3 Characteristic Zn K edge Quick-XANES spectra recorded at different temperatures during the LDH thermal decomposition. The spectra of nano-zno and nano-znal O 4 are also presented for comparison purpose. Fig. S4 Comparison of the EXAFS spectra measured at RT and corresponding FT of the Calc. LDH with the ones of a crystalline ZnO reference. 4 J. Name., 1,, 1-3 This journal is The Royal Society of Chemistry xx

Journal Name a) 1 3 4 5 6 R (Å) 5 6 4 3 6 4 1 Time (min) FT intensity (Å -4 ) b) 6 1 3 4 5 6 R (Å) Fig. S5 Evolution of FT of the Zn K edge EXAFS signals measured in situ during the LDH recovery at room temperature ( 5 C) after: (a)water and (b) 1 mg L -1 AB dye solution addition on the Calc-LDH. 5 4 3 8 6 4 1 Time (min) FT intensity (Å -4 ) This journal is The Royal Society of Chemistry xx J. Name., 13,, 1-3 5

Journal Name 1 Composition (%) 8 6 4 4 6 8 1 1 14 16 18 Time (min) Fig. S6 Percentages of Zn based species determined by MCR-ALS analysis of the Quick-XAS recorded at room temperature ( 5 o C) during recovery of LDH phase after addition of water and AB dye solution to Calc-LDH. H O ZnO LDH AB solution ZnO LDH 11.5 11. Fig. S7 Van't Hoff plot. ln (k ad ) 1.5 1. 9.5 9. 8.5 LDH Calc-LDH linear fit 3. 3.5 3.3 3.35 1 3 /T (K -1 ) 1% 93% 9% 91% 91% 15 q e (mg g -1 ) 1 5 1 3 4 5 Cycle number Fig. S8 Recyclability of the adsorbent Calc-LDH after AB adsorption. 6 J. Name., 1,, 1-3 This journal is The Royal Society of Chemistry xx

Journal Name Table S1 Best fitted EXAFS parameters of the LDH and Calc-LDH samples measured at RT. Italic parameters are fixed values. E = 9663 ev and S =.87 Sample N R (Å) (Å ) E (ev) R f (%) Bulk ZnO 4 O 1 Zn 1.96 ±.3 3.3 ±.3.44 ±.1.94 ±.11.7 ± 3.9 1.9 Pristine LDH 6. O ±.6 4.1 Zn ±.3 1.9 Al.5 ±.1 3.11 ±.1 3.9 ±.4.1 ±.1.154 ±.1.1164±.77 -.77 ±.3.9 Calc_Zn 3.9 O ±.5 1.1 Zn ±.8 1.96 ±.1 3.4 ±.1.56 ±.1.18 ±.5 1. ± 1..5 Table S Pseudo-second order kinetic model fitted parameters, and correlation coefficients for AB dye adsorption on LDH and Calc-LDH at 5 C. Pseudo-second order model Adsorbent k,1 (g mg -1 h -1 ) k, (g mg -1 h -1 ) q e1 (mg g -1 ) q e (mg g -1 ) R 1 R LDH 1.3 1 - ± 9.9 1-4 - 78.5 ± 3.34 -.997 - Calc-LDH 1.8 1 - ± 4.5 1-3 1.9 1-3 ± 9. 1-5 1177±11. 1351±5.334.994.989 Table S3 Langmuir isotherm model fitted parameters, q max and k L, and correlation coefficients, R L, for AB dye adsorption on LDH and Calc-LDH at different temperatures. Adsorbent T. ( C) q max (mg g -1 ) k L 1-3 (L mg -1 ) R L * LDH 5 61.8 39.998 Calc-LDH 5 1587 5.8.997 Calc-LDH 3 1615 7.3.998 Calc-LDH 35 1677 7.9.999 Calc-LDH 4 1693 9.8.999 Supplementary References 1. H. W. P. Carvalho, S. H. Pulcinelli, C. V. Santilli, F. Leroux, F. Meneau and V. Briois, Chemistry of Materials, 13, 5, 855-867.. W. H. Cassinelli, L. Martins, A. R. Passos, S. H. Pulcinelli, C. V. Santilli, A. Rochet and V. Briois, Catalysis Today, 14, 9, 114-1. 3. A. Voronov, A. Urakawa, W. v. Beek, N. E. Tsakoumis, H. Emerich and M. Rønning, Analytica Chimica Acta, 14, 84, -7. 4. J. Hong, E. Marceau, A. Y. Khodakov, L. Gaberová, A. Griboval-Constant, J.-S. Girardon, C. L. Fontaine and V. Briois, ACS Catalysis, 15, 5, 173-18. 5. A. Rochet, B. Baubet, V. Moizan, C. Pichon and V. Briois, Comptes Rendus Chimie, 16, 19, 1337-1351. 6. A. de Juan, J. Jaumot and R. Tauler, Analytical Methods, 14, 6, 4964-4976. 7. J. Jaumot, A. de Juan and R. Tauler, Chemometrics and Intelligent Laboratory Systems, 15, 14, 1-1. 8. W. Windig and J. Guilment, Analytical Chemistry, 1991, 63, 145-143. This journal is The Royal Society of Chemistry xx J. Name., 13,, 1-3 7