Microporous and Mesoporous Materials 126 (2009) 65–71 Contents lists available at ScienceDirect Microporous and Mesoporous Materials journal homepage: www.elsevier.com/locate/micromeso Synthesis and characterization of hybrid MCM-41 materials for heavy metal adsorption Kostas Dimos a,*, Panagiota Stathi b, Michael A. Karakassides a, Yiannis Deligiannakis b a b Department of Materials Science and Engineering, University of Ioannina, Ioannina 45110, Greece Department of Environmental and Natural Resources Management, University of Ioannina, Seferi 2, Agrinio 30100, Greece a r t i c l e i n f o Article history: Received 20 March 2009 Received in revised form 7 May 2009 Accepted 12 May 2009 Available online 21 May 2009 Keywords: Hybrid MCM-41 Dithiocarbamate Mesoporous Heavy metal adsorption a b s t r a c t A small dithiocarbamate molecule, N-(2-Aminoethyl)dithiocarbamate, was synthesized, characterized and afterwards used to modify and activate the surfaces of MCM-41 materials. The structure and the surface charge properties of the starting and the novel organic–inorganic hybrid mesoporous materials were studied by means of powder X-ray diffraction, Fourier transform infrared spectroscopy, DTA/TG thermal analyses, surface area measurements and potentiometric acid–base titrations. The hybrid materials retained the regular hexagonal arrangement of cylindrical pores which is the characteristic of the MCM-41 solids, while a high content (2.57 mmol/g) of the organic molecules in the final products was achieved. Despite the high concentration of the dithiocarbamate molecules in the pores of the hybrid MCM-41 materials, final solids retained high specific surface areas (632 m2/g) indicating a homogenous incorporation of the small organic molecules in the pores. A surface complexation model was developed to explain the results of the potentiometric titrations and to describe the surface charge and H-binding properties of the starting and final hybrid materials. These materials are promising heavy metal adsorbents due to the presence of the effective dithiocarbamate groups and the low pH value (3.2) of the point of zero charge. Ó 2009 Elsevier Inc. All rights reserved. 1. Introduction The discovery of the mesoporous materials family M41S at Mobil’s laboratories in 1992 [1,2] offered a new category of porous materials with many applications as catalysts [3,4], adsorbents [5,6], sensors [7] separators [8], etc. The most interesting M41S member is the MCM-41. The MCM-41 solids exhibit high specific surface areas (1000 m2/g), high crystallinity, high thermal stability, uniformity of hexagonal cylindrical pores, narrow pore distribution and regulated pore diameter from 15 to 100 Å. These characteristics render these solids as ideal heavy metal adsorbents [9–11]. The main disadvantage of MCM-41 is the lack of effective binding groups and permanent negative charge as in the case of clays. For this reason, in the last decades huge effort has been taken in the modification of the MCM-41 surface with thiol groups. In most cases, for the modification of mesoporous silicas, mercaptopropyltrimethoxysilane is used as thiol source. The final adsorbents are produced either by co-condensation [12–20] or by post-grafting [8–11,21–27], while the same molecules have been successfully used for the modification of clays [28–30]. Although the modification of porous materials with dithiocarbamate groups * Corresponding author. Tel.: +30 26510 97367; fax: +30 26510 97074. E-mail addresses: kdimos@cc.uoi.gr (K. Dimos), me01791@cc.uoi.gr (P. Stathi), mkarakas@cc.uoi.gr (M.A. Karakassides), ideligia@cc.uoi.gr (Y. Deligiannakis). 1387-1811/$ - see front matter Ó 2009 Elsevier Inc. All rights reserved. doi:10.1016/j.micromeso.2009.05.021 is of high importance, these groups are effective chelating agents for metal complexing and there has been an effort in the modification of clays [31], activated carbon [32] and mesoporous silicas [33–35]. In this aspect we report in this work the synthesis of a novel hybrid mesoporous material based on MCM-41. The MCM-41 material was modified by post-grafting of N-(2-Aminoethyl)dithiocarbamate (AEDTC) molecules on the pores surfaces of the mesoporous solid. The organic molecules of this substance were in a zwitterionic form and thereby their grafting was feasible by the silanol groups of the surfaces. AEDTC molecules were chosen in order not to block the MCM-41 pores. The final hybrid adsorbents were characterized with regard to their structural and surface charge properties. 2. Experimental 2.1. Reagents All materials were of reagent or analytical grade and were used as purchased without further purification. Tetraethylorthosilicate (TEOS) 98% was purchased from Sigma-Aldrich (131903), aqueous ammonia solution (NH3) 25%wt. from Fluka (09860), cetyltrimethylammonium bromide (CTAB) 95% from Sigma-Aldrich (855820), 66 K. Dimos et al. / Microporous and Mesoporous Materials 126 (2009) 65–71 ethanol (EtOH) 99.5% from Panreac (121086.1212), ammonium nitrate (NY4NJ3) 98+% from Sigma-Aldrich (221244), carbon disulfide (CS2) 99.5+% from Merck (1.02211.1000), ethylenediamine (H2N(CH2)2NH2) 99+% from Sigma-Aldrich (240729), diethyl ether (Et2O) 99+% from Fluka (31700), hydrochloric acid (HCl) 1N from Riedel de Haën (35328), sodium hydroxide pellets (NaOH) 99+% from Merck (1.06498.1000) and nitric acid (HNJ3) 65% from Riedel de Haën (30709). The solutions for the potentiometric titrations were prepared with ultra pure water (Milli-Q) by Milli-Q academic system with conductivity of demineralised water of 18.2 lS cm1. 2.2. Synthesis The MCM-41 sample was synthesized by hydrolyzing 50 g tetraethylorthosilicate (TEOS), added in one litre polyethylene bottle containing 417.5 g H2O, 268.5 g NH3 (25%wt) and 10.5 g cetyltrimethylammonium bromide (CTAB). Each of the previous additions was stirred for 30 min. The product was retrieved after heat treatment at 80 °C for 96 h, which can be slightly considered as a hydrothermal treatment. It was filtered, rinsed with cold ethanol (EtOH) and finally placed on a plate for air-drying (sample: MCM-41). Afterwards it was treated with NH4NO3 in EtOH for 30 min at 70 °C for the removal of the surfactant molecules, filtered, rinsed with cold EtOH and the same procedure was repeated. Finally the end product was placed on a plate for air-drying (sample: MCM-41NH4) [36]. A solution of CS2 (0.95 g, 0.0125 mol) in EtOH (50 g) was added dropwise to a solution of H2N–CH2–CH2–NH2 (0.75 g, 0.0125 mol) in EtOH (50 g) at 5 °C to synthesize N-(2-Aminoethyl)dithiocarbamate. After stirring for one hour the retrieved white powder was filtered, rinsed with cold EtOH and ether (Et2O) and dried under vacuum. The retrieved powder was dissolved in hot H2O and recrystallized at RT. The white crystals were rinsed with EtOH and Et2O, dried under vacuum and finally ground so that it was acquired as powder [37]. The synthesis of the zwitterionic form (inner salt) of the N-(2-Aminoethyl)dithiocarbamic acid (AEDTC) was achieved via the following chemical reaction: H2 NACH2 ACH2 ANH2 þ CS2 ! H3 Nþ ACH2 ACH2 ANðHÞACS2 ð1Þ The synthesis of the hybrid material was carried out with the heat treatment of 400 mg MCM-41NH4 in 75 ml EtOH at 50 °C for 2 h with 300 mg AEDTC and addition of 5 ml HCl 1 N for the dissolution of the organic molecule in EtOH. The final product was isolated by filtration, rinsed with EtOH and dried at RT (sample: MCM-41AEDTC). KBr pellets and were used for recording the spectra, which were the average of 64 scans at 2 cm1 resolution. X-ray powder diffraction data were collected on a D8 Advance Bruker diffractometer using Cu Ka (40 kV, 40 mA, k = 1.54178 Å) radiation and a secondary beam graphite monochromator. Diffraction patterns were collected in the 2h range from 2 to 80 degrees, in steps of 0.02 degrees and 2 s counting time per step. The nitrogen adsorption–desorption isotherms were measured at 77 K on a Sorptomatic 1990, thermo Finnigan porosimeter. Specific surface areas SBET were determined by the Brunauer–Emmett–Teller (BET) method using adsorption data points in the relative pressure P/Po range 0.01–0.30. Surface areas St were also determined from t-plots which were constructed using nitrogen adsorption data on a nonporous-hydroxylated silica standard. The desorption branches of the isotherms were used for the pore size calculations according to the Kelvin equation rk 4.146/log Po/P (Å), where Po is the saturated vapour pressure in equilibrium with the adsorbate condensed in a capillary or a pore, P is the vapour pressure of liquid contained in a cylindrical capillary, and rk is the Kelvin radius of the capillary or pore. The Kelvin equation was used according to BJH method for the calculation of core radii from the pressure values of the isotherm, the pore radius combining the last with the t-values from the standard isotherm and finally the pore size distribution (PSD) of the samples. All samples used for the surface analyses were outgassed at 250 °C for 10 h under high vacuum (105 mbar) before the measurements. The surface charge properties of the starting and the hybrid materials (MCM-41NH4 and MCM-41AEDTC) were evaluated by potentiometric acid–base titrations. Acid–base potentiometric titrations were used to measure the surface proton adsorption as described earlier [38,39]. A 12.5 mg portion of material was suspended in a titration cell containing 12.5 mL of Milli-Q water to yield material concentration 1 g/L. The suspension allowed to equilibrate for 30 min under continuous stirring and purged with N2 prior to the titration. Then it was divided into two equal volume portions, one each for the alkalimetric and acidimetric titrations. The alkalimetric titrations were performed with 12.5 mM NaOH and the acidimetric titrations with 12.5 mM HNO3. In all titrations the Metrohm 794 Basic Titrino burette was used and the pH was measured with Metrohm Pt-glass electrode type (6.0239.100). The titration experiments were repeated in triplicate. A key parameter in this type of experiments is the achievement of thermodynamic equilibrium after each acid–base addition. In our setup a stability of ±0.01 mV in the electrode reading was required, corresponding to a stability of ±0.05 at pH values. Typically in the present experiment, pH equilibrium was attained within 20 min after each acid–base addition. 2.3. Characterization Single-crystal X-rays diffraction study of the organic substance (AEDTC) was performed with a Bruker P4 diffractometer using Mo Ka (50 kV, 40 mA, k = 0.71073 Å) radiation with a suitable single crystal (0.45 0.30 0.15 mm). AEDTC was also studied by means of NMR spectroscopy, elemental analysis, thermal analyses and infrared spectroscopy. Nuclear Magnetic Resonance spectra were recorded with a Bruker AC at 250 MHz, using D2O + NaOH as solvent. Elemental analysis was performed with a CHNS Perkin Elmer 2400 II Elemental Analyzer. Thermal analyses were studied with a Perkin Elmer Pyris Diamond TG/DTA analyser in atmosphere with a 3 °C/min heating rate up to 800 °C while the melting point of the substance was determined with a Stuart Scientific melting point apparatus. Infrared spectra were measured on a Perkin Elmer GX, Fourier transform spectrometer in the frequency range of 400– 4000 cm1. Samples were dispersed, pulverized in the form of 3. Results and discussion 3.1. AEDTC characterization Single crystal X-rays diffraction for AEDTC gave the following data: Monoclinic, P21/c, a = 6.990 (3) Å, b = 10.160 (5) Å, c = 8.688 (4) Å, a = 90.04 (3)o, b = 92.51 (2)o, c = 90.00 (2)° and V = 616.08 (9) Å3. These data come in full agreement with those reported by Yamin et al. about the crystallography of N-(2-Aminoethyl)dithiocarbamic acid (AEDTC) [37], confirming the synthesis of the zwitterionic form of AEDTC. Powder X-ray diffraction pattern of the substance is available as supplementary material. 1H NMR spectra, also available as supplementary material, resulted: dH(250 MHz; D2O + NaOH; Me4Si) 2.70 (2 H, t, J 6.25, N(D2)CH2) and 3.49 (2 H, 1 t, J 6.25, CH2N(D)CS 2 ). H NMR data come also in full agreement with those reported in Ref. [40]. K. Dimos et al. / Microporous and Mesoporous Materials 126 (2009) 65–71 67 The melting point of the organic substance AEDTC was found 193 °C (from H2O) which is very reasonable compared to the reported AEDTC sodium salt mp of 201 °C [41,42]. The results above are confirmed by the elemental analysis of the sample (Found: C, 26.58; H, 5.80; N, 20.43; S, 47.19. Calc. for C3H8N2S2: C, 26.45; H, 5.92; N, 20.56; S, 47.07%). FT-Infrared spectrum of AEDTC in Fig. 1 showed main peaks at mmax(KBr pellets)/cm1: 3310w m(NH), 3231vs m(NH3+), 2940br masym.(CH2), 2851br msym.(CH2), 1585s d(NH), 1508vs m(N CS2 ), 1478vs m(CN), 1442s d(CH2) and 1005vs m(C S) [43,44]. The shift of the N CS 2 band at higher frequency and respectively of the C S band at lower frequency indicate that the molecule has three resonance forms [44]. 3.2. Structural study of starting and hybrid materials FT-Infrared spectra (a) and (b) of MCM-41NH4 and MCM41AEDTC, respectively, are shown in Fig. 1. The two spectra have common peaks at mmax(KBr pellets)/cm1: 3473br m(H2O), 1639w d(H2O), 1235w masym.(Si–O–Si) longitudinal-optical mode, 1087vs masym.(Si–O–Si) transverse-optical mode, 960 m masym.(Si–OY), 800 m d(Si–O–Si) and 463s q(Si–O–Si) [45,46]. Spectrum (b) of MCM-41AEDTC has additional peaks assigned to the organic molecules AEDTC. In particular, the spectrum of the hybrid material has a shoulder in its main peak at 1005 cm1 which is attributed to m(C S). Moreover distinct peaks at 1505 and 1590 cm1 are assigned as m(N CS 2 ) and d(NH), respectively. Spectrum (b) has common peaks with spectrum (c) also in the region 2400–3250 cm1. Spectral pattern in this region has a fingerprint character of the AEDTC presence in the hybrid material. The above indicate the successful importation of the organic molecules in the MCM-41 pores. X-ray powder diffraction patterns of the samples MCM-41, MCM-41NH4 and MCM-41AEDTC within the 2h range 1.5°–7° are shown in Fig. 2. Those are typical of MCM-41 samples with the characteristic strong reflection at low scattering angles 2h (2o) corresponding to a d100 spacing at about 39.9, 41.5 and 41.6 Å using Bragg’s law, respectively. The fact that all three samples show the reflections which correspond to d110, d200 and even d210 spacings indicates that the MCM-41 structure is maintained in both (NH4 and AEDTC) cases providing good quality and high range hexagonal uniform pores. Thermal analysis of the final product (MCM-41AEDTC) indicates the presence of dithiocarbamate groups inside MCM-41 pores as suggested by the decrease of %TG signal (35%wt) in the temperature range of 200 to 300 °C. Also, in the DTA signal an exo- Fig. 1. FT-Infrared spectra of MCM-41NH4 (a), MCM-41AEDTC (b) and AEDTC (c). Fig. 2. X-ray diffraction patterns in the low angle region for the MCM-41 matrix for samples MCM-41 (a), MCM-41NH4 (b) and MCM-41AEDTC (c). thermic peak appears at 292 °C, which originates from the combustion of the organic substance. On the other hand, the small inset in Fig. 3 shows the %TG signal of the MCM-41NH4 sample in which the corresponding loss of weight at temperatures 200– 300 °C is only 2%. This is due to the low gram-equivalent weight (18 g/greq) of NH4+ in comparison with the high AEDTC molecular weight (136.24 g/mol) and thus the NH4+ including compound is giving smaller %TG signal losses. Moreover, NH4+ is decomposed in an extended thermal region in contrary to the combustion of AEDTC molecules which is observed in the range of 200–300 °C. Thus the above suggests that the 35%wt loss of the hybrid material is due to the presence of the organic molecules. The small endothermic peak at 163 °C in the DTA signal is believed to originate from molecule deformation as no respective weight loss is Fig. 3. DTA/TG diagrams of the MCM-41AEDTC sample. Inset: %TG diagram of the MCM-41NH4 sample. 68 K. Dimos et al. / Microporous and Mesoporous Materials 126 (2009) 65–71 Table 2 Reactions and stability constants (pK) used to fit the experimental data. pKa Reaction (De-)protonation reactions of MCM-41NH4 3 {JY + H + M XOHþ 2 4 {JY M {J + Y+ + + 9 NY4 M NY3 + Y Deprotonation reaction of MCM-41AEDTC 10 AEDTC-H M AEDTC + H+ a Fig. 4. Nitrogen adsorption–desorption isotherms for MCM-41NH4 (a) and MCM41AEDTC (b). Inset: pore distributions calculated from N2 desorption branches. observed. The hybrid’s material high loading with AEDTC is due to the small carbon chain length of the organic molecules which prevents the pore blocking and thus fills in a high percentage. Moreover, it has been shown that MCM-41 materials have a varying hydroxyl group concentration on the pores surface and authors have estimated at aJY: 3 lmol/m2 [47], while others at 0 aJY : 4.5 lmol/m2 [48]. Considering that these materials have specific surface area at about 1000 m2/g, these values can be converted to aJY: 3 mmol/g and aJY’: 4.5 mmol/g, respectively. Given that the hybrid material has a 35%wt. organic content and that the AEDTC molecular weight is 136.24 g/mol, it is concluded that the AEDTC content in the hybrid material is 2.57 mmol/g. Comparison of this value with the previous values of the hydroxyl groups concentration on the pores surface, which are responsible for the AEDTC grafting, shows that the hybrid’s material completeness in AEDTC may have reached even 85%, leaving intact the pore system structure as observed by other characterization techniques. The completeness percentage would have been even bigger if the ion exchange reactions with the AEDTC molecules in the synthesis of the hybrid material were repeated. However this treatment was not repeated in order to retain the high crystallinity in the final hybrid material. The nitrogen adsorption–desorption isotherms of the samples MCM-41NH4 and MCM-41AEDTC are shown in Fig. 4. Both the samples have type IV classification isotherms [49], which is the characteristic of adsorption of mesoporous materials MCM41. The presence of a sharp sorption step in adsorption curves, near to a 0.3 value of P/Po indicates that both solids possess a well-defined array of regular mesopores. Specific surface area was calculated using BET equation and was found to be 948 m2/g for the MCM-41NH4 and 632 m2/g for the MCM-41AEDTC sample and from t-plots 937 m2/g and 647 m2/g respectively [50,51]. This 33% decrease of the specific surface area provides evidence that the pores are filled with the organic molecule which has a significant bigger volume from the NHþ 4 cations without blocking the pores. The fact that the isotherm for the MCM-41AEDTC sample is similar in shape to that of the parent sample, suggests that the organic molecules should be dispersed uniformly throughout the pores. The desorption branch was used to calculate mesopore size 1.6 5.0 9.3 6.9 Errors, pK: ±0.2. distributions by means of the Barrett-Joyner-Halenda (BJH) method [52]. From the PDS curve of the MCM-41NH4 sample its mean pore diameter was calculated at about 27.1 Å, while the pores of the MCM-41AEDTC sample show a size distribution with an average pore diameter of 26.4 Å (Fig. 4 inset). Nevertheless it is a fact that the BJH method tends to underestimate pore diameter [53], so the Kruk–Jaroniec–Sayari (KJS) geometrical model was also used for the pore diameter calculation [54,55], though this model slightly overestimates the diameter. The KJS geometrical model is based on the following formula: W KJS ¼ c d100 ½q V p =ð1 þ q V p Þ1=2 ð2Þ ½ ½ where wKJS is the pore diameter, c = [8 / (3 p)] = 1.213 is a constant, d100 is the (1 0 0) interplanar spacing, q is the density of pore walls (taken as the density of amorphous silica, 2.2 g/cm3) and Vp is the pore volume, equal to 0.80 cm3/g and 0.54 cm3/g for MCM41NH4 and MCM-41AEDTC samples, respectively, as estimated from the nitrogen adsorption–desorption isotherms (Table 1). The formula gives a diameter equal to 40.2 Å for MCM-41NH4 and to 37.2 Å for MCM-41AEDTC. These values highly differ from the BJH method calculated, which in reality means that actual pore diameter is somewhere between the two calculated values. The most significant pore parameters derived from X-ray diffraction patterns and N2 adsorption data for the two samples are listed in Table 1. 3.3. Surface charge properties of starting and hybrid materials The H-binding properties of the surface groups of the MCM materials used in this work were described by the Diffuse Layer Model (DLM) which is a surface complexation model. Surface Complexation Models (SCMs) can model successfully the adsorption of ions on charged surfaces by assuming that adsorption involves both a coordination reaction at specific surface sites and an interaction between the adsorbed ions and the organic ligand on the modified material [56]. FITEQL 4.0 [57] was used to determine the best fit of various surface complexation reactions or combinations of reactions to the experimental adsorption data. The Davies equation was used to calculate the activity coefficient [56]. Relative errors of 5% in the concentration of surface sites and pH were allowed in FITEQL input values. All the pertinent reactions at the solid solution interface and their pK values, used for the fit of the experimental H-binding data are listed in Table 2. Štamberg et al. have successfully used SCM to describe the Hbinding properties of an MCM-41 material [58]. In our modelling Table 1 Pore parameters derived from X-ray diffraction patterns and N2 adsorption data. Samples SBET (m2/g) St (m2/g) Vpore (cm3/g) d100 (Å) ao (Å) dBJH (Å) wKJS (Å) p (Å) MCM-41NY4 MCM-41AEDTC 948 632 937 647 0.80 0.54 41.5 41.6 47.9 48.0 27.1 26.4 40.2 37.2 20.8/7.7 21.6/10.8 K. Dimos et al. / Microporous and Mesoporous Materials 126 (2009) 65–71 69 we have assumed three different populations of H-binding sites on the starting and the hybrid materials, XOH sites (a), NHþ 4 (b) and AEDTC groups (c). XOH sites represent the amphoteric hydroxyl groups on the MCM-41 surface. H-exchange at the surface hydroxyl sites of MCM-41 can be modelled according to reactions (3) and (4): Kþ int XOH þ HþS $ XOHþ2 ð3Þ K int XOH $ XO þ HþS ð4Þ Hþ s where describes the protons near the charged solid surface [56]. According to this model, at any pH value the total concentration of surface groups XOH is given by Eq. (5): Rð XOHÞ ¼ ½ XOH þ ½ XO þ ½ XOHþ2 ð5Þ Depending on pH of the solution, a surface site can be at neutral, protonated, or deprotonated form. The pH where [{JY2+] = [{J] is the Point of Zero Charge [56]. The equilibrium constants for the surface reactions are given by Eqs. (6) and (7): F W ½ XOHþ2 0 RT e ½ XOHðHþS Þ ½ XO ðHþS Þ FRTW0 ¼ e ½ XOH Kþint ¼ ð6Þ K int ð7Þ where W0 is the electrostatic surface potential [56], F is the Faraday constant, R is the gas constant and T is the absolute temperature. The relation of the surface charge r with W0 is given by the Gouy –Chapman equation (8): r ¼ 0:1174 I1=2 sin h W0 F 2RT ð8Þ where I is the ionic strength. The H-binding reaction of the NHþ 4 counterions is shown in the following (9): NHþ4 þ $ NH3 þ H ð9Þ The protonation of AEDTC groups (third binding population sites) on the hybrid material was described by the following reaction (10): AEDTC H $ AEDTC þ H ð10Þ where the symbol () has been added to notify that the AEDTC moieties are considered as part of the solid matrix. Of importance is to notice that the pK for the protonation of the AEDTC in reaction (10) (Table 2) has to be determined by the fit to the acid–base titration data. This implies that we consider that the pK of the AEDTC attached on the solid matrix might differ from the, known [59], pK in solution. Fig. 5A, top, shows the acid–base potentiometric titration experimental data and the theoretical fit for sample MCM41NH4. CA and CB in the vertical axis of Fig. 5A represent the acid or base addition to the two solution portions used for the acidimetric and alkalimetric titrations, respectively. The term CA–CB has no physical meaning but is used as we combine the data from the two titrations in one common diagram. At pH 3–4 we observe a rapid loss of protons from the surface groups resisting the pH increase with base addition. Those protons derive from the deprotonation reaction (4) of the XOH sites. In the pH region 4–9 the slightest base addition launches the pH value, indicating that all XOH sites have converted to {J. Eventually at pH > 9 the sample MCM41NH4 resists again at the pH increase due to deprotonation reaction (9) of the NHþ 4 counterions. The theoretical fit anticipates the pK values of the three participating reactions (3), (4), and (9). Those Fig. 5. Potentiometric acid–base titration (symbols) and theoretical fit (solid line) for sample MCM-41NH4 (A) and speciation analysis of the surface species derived by using the parameters in Table 2 (B). values are: pKint+ = 1.6 ± 0.2 for reaction (3), pKint = 5.0 ± 0.2 for reaction (4) and pK = 9.3 ± 0.2 for reaction (9), also listed in Table 2. The estimated pK int value is 3.7 less than analogous pK values for MCM-41 material [58], a fact with great physical meaning which will be discussed later. The pH of the Point of Zero Charge can be estimated from the following Eq. (11): pHpzc ¼ 1=2ðjpKþint j þ jpKint jÞ ¼ 3:2 0:2 ð11Þ This value is among the lowest PZC reported for oxides bearing protonable surface groups [60]. This implies that in aqueous solution at any pH value above 3.2 the {J species will dominate and the MCM-41 surface will bear a progressively increasing negative charge, e.g. which is counterbalanced by the NHþ 4 cations. The physical meaning of the low pHPZC value is that the material is a very promising adsorbent in a wide pH range as it bears negative charge at pH > 3.2. The above can be visualized by the speciation analysis, displayed in Fig. 5B. Fig. 6A, top, shows the acid–base potentiometric titration experimental data and the theoretical fit for sample MCM41AEDTC. By comparing the curves in Figs. 5A and 6A we notice that the incorporation of the AEDTC in the MCM-41 pores has two significant effects on the H-binding properties of the final hybrid material. First, the NHþ 4 ions are largely exchanged by the zwitterions H3N+–CH2–CH2–N(H)–CS 2 as evidenced by their loss in the Hbinding data for MCM-41AEDTC. Second and the main difference, is the loss of protons at pH 5–7. As we show by the theoretical fit to the data, solid line in Fig. 6A, this is due to the deprotonation of the R–CS2 groups, reaction (10) in Table 2, with a pK value of 6.9. This pK value is considerably lower than the 3.3 reported previously 70 K. Dimos et al. / Microporous and Mesoporous Materials 126 (2009) 65–71 surface area (632 m2/g) while the AEDTC content reached 35%wt. Moreover the study of the surface charge properties of the hybrid material resulted a significant low pH of the point of zero charge (pHPZC = 3.2). These results render the hybrid material as a promising heavy metal adsorbent regarding also the AEDTC presence in the pores of the MCM-41 solid. Heavy metal adsorption experiments by the hybrid material are currently carried out in our laboratory. Acknowledgments This research was co-funded by the European Union in the framework of the program ‘‘Pythagoras I” of the ‘‘Operational Program for Education and Initial Vocational Training” of the 3rd Community Support Framework of the Hellenic Ministry of Education, funded by 25% from national sources and by 75% from the European Social Fund (ESF). We would like to thank the X-ray Laboratory and the NMR Centre of the University of Ioannina for measurements. Helpful and stimulating discussions with Ass. Prof. M. Siskos and Lecturer Dr. I. Koutselas are gratefully acknowledged. Appendix A. Supplementary data 250 Hz 1H NMR spectra of AEDTC on Figs. S1 and S2, experimental and simulated X-ray powder diffraction patterns of AEDTC on Fig. S3. Supplementary data associated with this article can be found, in the online version, at doi:10.1016/j.micromeso.2009. 05.021. References Fig. 6. Potentiometric acid–base titration (symbols) and theoretical fit (solid line) for sample MCM-41AEDTC (A) and speciation analysis of the surface species derived by using the parameters in Table 2 (B). [31] for a dithiocarbamate in clay. The difference in the pK values is not trivial to explain. We may speculate that local electrostatic interactions of the zwitterionic form H3N+–CH2–CH2–N(H)–CS 2 inside the MCM-41 tubes are responsible for the stabilisation of the H – binding on the –CS 2 moiety as evidenced by the low pK. The resulting speciation, Fig. 6B, helps to visualize all the protonation events. At pH > 3 the surface sites are in the form XO. Accordingly, at pH < 8 a fraction of 10–15% of NH3 is formed. The speciation in Fig. 6B shows that in the hybrid material MCM41AEDTC, nearly 30% of the initial NHþ 4 ions are still present, i.e. non-exchanged by the AEDTC, while the other 70+% of the {J sites are occupied by the AEDTC molecules. From the concentration of the hybrid material (1 g/L) and the AEDTC groups (2.12 mM) in the titration solutions, the hybrid’s material content in AEDTC can be estimated, which results in a 2.12 mmol/g content. This value is considered underestimated as from the thermogravimetric analysis the content was estimated at 2.57 mmol/g, a value, most likely, closer to reality. Of primary importance, however is the role of the R–CS 2 groups of the AEDTC moieties which at pH > 6 are gradually becoming dominant. These groups are effective chelating agents for metal complexing, making the hybrid material an ideal heavy metal adsorbent. 4. Conclusions In the present work a novel hybrid mesoporous material was synthesized based on MCM-41 and the organic molecule N-(2Aminoethyl)dithiocarbamate (AEDTC). The hybrid material retained its structure properties, i.e. the high crystallinity and high [1] C.T. Kresge, M.E. Leonowicz, W.J. Roth, J.C. Vartuli, J.S. Beck, Nature 359 (1992) 710. [2] J.S. Beck, J.C. Vartuli, W.J. Roth, M.E. Leonowicz, C.T. Kresge, K.D. Schmitt, C.TW. Chu, D.H. Olson, E.W. Sheppard, S.B. McCullen, J.B. Higgins, J.L. Schlenker, J. Am. Chem. Soc. 114 (1992) 10834. [3] A. Corma, Chem. Rev. 97 (1997) 2373. [4] A. Taguchi, F. Schuth, Micropor. Mesopor. Mater. 77 (2005) 1. [5] J.C. Vartuli, A. Malek, W.J. Roth, C.T. Kresge, S.B. McCullen, Micropor. Mesopor. Mater. 44–45 (2001) 691. [6] D. Perez-Quintanilla, I. Del Hierro, M. Fajardo, I. Sierra, J. Mater. Chem. 16 (2006) 1757. [7] H.S. Zhou, H. Sasabe, I. Honma, J. Mater. Chem. 8 (1998) 515. [8] X. Feng, G.E. Fryxell, L.-Q. Wang, A.Y. Kim, J. Liu, K.M. Kemner, Science 276 (1997) 923. [9] K.F. Lam, K.L. Yeung, G. McKay, Langmuir 22 (2006) 9632. [10] A.M. Liu, K. Hidajat, S. Kawi, D.Y. Zhao, Chem. Commun. (2000) 1145. [11] L. Mercier, T.J. Pinnavaia, Environ. Sci. Technol. 32 (1998) 2749. [12] J. Shah, T.J. Pinnavaia, Chem. Mater. 17 (2005) 947. [13] J. Shah, T.J. Pinnavaia, Chem. Commun. (2005) 1598. [14] A. Walcarius, C. Delacote, Anal. Chem. Acta 547 (2005) 3. [15] A. Walcarius, C. Delacote, Chem. Mater. 15 (2003) 4181. [16] Q. Yang, J. Liu, J. Yang, L. Zhang, Z. Feng, J. Zhang, C. Li, Micropor. Mesopor. Mater. 77 (2005) 257. [17] Q. Wei, Z. Nie, Y. Hao, Z. Chen, J. Zou, W. Wang, Mater. Lett. 59 (2005) 3611. [18] S.J.L. Billinge, E.J. McKimmy, M. Shatnawi, H. Kim, V. Petkov, D. Wermeille, T.J. Pinnavaia, J. Am. Chem. Soc. 127 (2005) 8492. [19] D. Liu, J.-H. Lei, L.-P. Guo, X.-D. Du, K. Zeng, Micropor. Mesopor. Mater. 117 (2009) 67. [20] J. Brown, R. Richer, L. Mercier, Micropor. Mesopor. Mater. 37 (2000) 41. [21] J. Liu, X. Feng, G.E. Fryxell, L.-Q. Wang, A.Y. Kim, M. Gong, Adv. Mater. 10 (1998) 161. [22] X. Chen, X. Feng, J. Liu, G.E. Fryxell, M. Gong, Sep. Sci. Technol. 34 (1999) 1121. [23] S.V. Mattigod, X. Feng, G.E. Fryxell, J. Liu, M. Gong, Sep. Sci. Technol. 34 (1999) 2329. [24] G.E. Fryxell, S.V. Mattigod, Y. Lin, H. Wu, S. Fiskum, K. Parker, F. Zheng, W. Yantasee, T.S. Zemanian, R.S. Addleman, J. Liu, K. Kemner, S. Kelly, X. Feng, J. Mater. Chem. 17 (2007) 2863. [25] A. Walcarius, M. Etienne, J. Bessiere, Chem. Mater. 14 (2002) 2757. [26] A. Walcarius, M. Etienne, B. Lebeau, Chem. Mater. 15 (2003) 2161. [27] J. Brown, L. Mercier, T.J. Pinnavaia, Chem. Commun. (1999) 69. [28] L. Mercier, C. Detellier, Environ. Sci. Technol. 29 (1995) 1318. [29] L. Mercier, T.J. Pinnavaia, Micropor. Mesopor. Mater. 20 (1998) 101. [30] A.de M.F. Guimaraes, V.S.T. Ciminelli, W.L. Vasconcelos, Appl. Clay Sci. 42 (2009) 410. K. Dimos et al. / Microporous and Mesoporous Materials 126 (2009) 65–71 [31] P. Stathi, K. Litina, D. Gournis, T.S. Giannopoulos, Y. Deligiannakis, J. Colloid Interface Sci. 316 (2007) 298. [32] L. Monser, N. Adhoum, Sep. Purif. Technol. 26 (2002) 137. [33] K.A. Venkatesan, T.G. Srinivasan, P.R. Vasudeva Rao, J. Radioanal. Nucl. Chem. 256 (2003) 213. [34] K.A. Venkatesan, T.G. Srinivasan, P.R. Vasudeva Rao, Colloids Surf., A 180 (2001) 277. [35] K.A. Venkatesan, T.G. Srinivasan, P.R. Vasudeva Rao, Sep. Sci. Technol. 37 (2002) 1417. [36] K. Dimos, I.B. Koutselas, M.A. Karakassides, J. Phys. Chem. B 110 (2006) 22339. [37] B.M. Yamin, M.A. Kadir, M.Z.M. Zin, A. Usman, I.A. Razak, H-K. Fun, Acta Cryst. E58 (2002) o293. [38] E. Giannakopoulos, P. Stathi, K. Dimos, D. Gournis, Y. Sanakis, Y. Deligiannakis, Langmuir 22 (2006) 6863. [39] P. Stathi, K.C. Christoforidis, A. Tsipis, D.G. Hela, Y. Deligiannakis, Environ. Sci. Technol. 40 (2006) 221. [40] K.J. Ivin, E.D. Lillie, Makromol. Chem. 179 (1978) 591. [41] A.Y. Yakubovich, V.A. Klimova, J. Gen. Chem. USSR 9 (1939) 1777; A.Y. Yakubovich, V.A. Klimova, Chem. Abstr. 34 (1940) 3685. [42] W.D. Marshall, J. Agric. Food Chem. 25 (1977) 357. [43] C. Chieh, S.K. Cheung, Can. J. Chem. 59 (1981) 2746. [44] P. Deplano, E.F. Trogu, A. Lai, Inorg. Chim. Acta 68 (1983) 147. [45] M.A. Karakassides, D. Petridis, D. Gournis, Clays Clay Miner. 45 (1997) 649. [46] R.M. Almeida, T.A. Guiton, C.G. Pantano, J. Non-Cryst. Solids 121 (1990) 193. 71 [47] D. Kumar, K. Schumacher, C.du F. von Hohenesche, M. Grün, K.K. Unger, Colloids Surf., A 187–188 (2001) 109. [48] X.S. Zhao, G.Q. Lu, A.K. Whittaker, G.J. Millar, H.Y. Zhu, J. Phys. Chem. B 101 (1997) 6525. [49] K.S.W. Sing, D.H. Everett, R.A.W. Haul, L. Moscou, R.A. Pierotti, J. Rouquerol, T. Siemieniewska, Pure Appl. Chem. 57 (1985) 603. [50] B.C. Lippens, J.H. De Boer, J. Catal. 4 (1965) 319. [51] M.R. Bhambhani, P.A. Cutting, K.S.W. Sing, D.H. Turk, J. Colloid Interface Sci. 38 (1972) 109. [52] E.P. Barrett, L.G. Joyner, P.P. Halenda, J. Am. Chem. Soc. 73 (1951) 373. [53] W. Zhang, C.I. Ratcliffe, I.L. Moudrakovski, J.S. Tse, C.-Y. Mou, J.A. Ripmeester, Micropor. Mesopor. Mater. 79 (2005) 195. [54] M. Kruk, M. Jaroniec, A. Sayari, J. Phys. Chem. B 101 (1997) 583. [55] M. Kruk, M. Jaroniec, A. Sayari, Micropor. Mesopor. Mater. 27 (1999) 217. [56] D.A. Dzombak, F.M.M. Morel, Surface Complexation Model, John Willey & Sons, New York, 1990. [57] A. Herbelin, J. Westall, FITEQL: A computer program for determination of chemical equilibrium constant from experimental data, Version 4.0, Report 9901, Department of Chemistry, Oregon State University: Corvallis, Oregon, 1999. [58] K. Štamberg, K.A. Venkatesan, P.R. Vasudeva Rao, Colloids Surf., A 221 (2003) 149. [59] K.I. Aspila, C.L. Chakrabarti, V.S. Sastri, Anal. Chem. 45 (1973) 363. [60] M. Kosmulski, Chemical Properties of Material Surfaces, Marcel Dekker Inc., New York, 2001.