Initial solutions with concentration of 1 mg/ml were prepared by dissolving of precise sample weights of the Analar grade salts (NH₄)₆Mo₇O₂₄∙4H₂O, (NH₄)₂Cr₂O₇, Na₂WO₄∙2H₂O, NH₄VO₃, ZnCl₂, Pb(NO₃)₂, CuCl₂・2H₂O, Cd(NO₃)₂∙4H₂O and Co(NO₃)₂∙6H₂O by method described in [12] . Working solutions were prepared from the initial ones immediately before experiments. The necessary standard solutions of acids and buffers were prepared from appropriate concentrates (FIXANAL^Ò, Sigma-Aldrich).

The Analar grade 3-aminopropyltriethoxysilane, guanidine hydrochloride and absolute toluene were used for synthesis of new adsorbent. Chemical binding of guanidine to the silica surface was carried out in two stages. Silica gel (Merck) with the specific surface area of 256 m²/g, pore size of 12 nm and particles diameter of 0.1 - 0.2 mm was used as a carrier.

At the first stage, amino-grafted silica gel was obtained by chemical modification of surface with solution of 3-aminopropyltriethoxysilane in toluene. Initial silica sample (70 g) was preliminarily dried at 200˚C for 2 h. Then silica was placed in three-necked round bottom reactor with a thermometer and a reflux condenser and suspended in 250 ml of absolute toluene, then 14 ml of 3-aminopropyltriethoxysilane was added under constant stirring. Reaction mixture was refluxed at the toluene boiling temperature for 2 h. Obtained amino-grafted silica (aminosilica) was then filtered and after 5 times washing with 50 ml toluene and dried under vacuum at 100˚C - 110˚C. The concentration of grafted amino groups (1.0 mmol/g) was estimated by titrimetry with sodium hydroxide.

At the second stage chemical binding of guanidine hydrochloride was carried out. 20 g of aminosilica was placed in three-necked round bottom reactor with a thermometer, a reflux condenser, oil bath and mixer and suspended in 30 ml of distilled water, then solution of 1.53 g (0.016 mol) of guanidine hydrochloride in 5 ml of distilled water was added under constant stirring.

The reaction mixture was heated and kept at 70˚C - 95˚C for 2 h. Then the temperature was gradually raised to 150˚C during 3 h, facilitated removal of water. When the reaction mixture had become almost dry, mixer was switched off, but the mixture was kept at temperature of 150˚C - 160˚C for 2 h.

The fact of the condensation reaction running and successful binding of guanidine hydrochloride on the aminosilica surface was qualitatively detected by elimination of ammonia and by tracking changes of pH of the reaction mixture from a weakly alkaline (pH = 7.3) to alkaline (pH = 8.5) (Scheme 1).

Scheme 1. Covalent binding of guanidine hydrochloride on the surface of modified amino-grafted silica.

IR-spectrum of the synthesized adsorbent was investigated and compared with IR-spectrum of guanidine hydrochloride to confirm its covalent binding on the surface of modified amino-grafted silica. Spectra were registered using Nicolet Nexus 470 FT-IR spectrometer. The structure of guanidine hydrochloride is very similar to the structure of amino-grafted silica. However, the characteristic band of -groups stretching vibrations at 2400 cm⁻¹ is typical for guanidine hydrochloride [13] . This characteristic band is also presented in the IR-spectrum of the synthesized adsorbent, as opposed to the IR-spectrum of amino-grafted silica. This fact also proof successful anchorage of guanidine hydrochloride on aminosilica surface.

The concentration of bound guanidine was determined by thermogravimetry.

According to thermogravimetric data the difference in weight loss of the sample between the first and second stage of the synthesis was 7.3%. This weight loss can be attributed to the binding of guanidine hydrochloride on the surface of modified silica. The concentration of chemically bound guanidine hydrochloride, which was calculated from the obtained data, is 75 mg/g (0.95 mmol/g) of silica. The degree of conversion of surface aminogroups is 95%.

The degree of ions adsorption (R) was calculated using the formula:

where m_o is a weight of introduced metal, m_ads is a weight of adsorbed metal, m is a weight of metal in equilibrium solution, calculated as m = С∙V, where С is an equilibrium concentration and V is an equilibrium volume.

Photometric measurements of equilibrium concentrations (С) of working solutions were conducted using spectrophotometer SF-46 (LOMO, Russia), in a quartz cell with path length of 10 mm at 540 nm for Cr(VI), 470 nm for Mo(VI), 610 nm for W(VI), 490 nm for V(V) and Cu(II), 495 nm for Zn(II), 520 nm for Pb(II) and 500 nm for Co(II) and Cd(II) according to methods described in [14] - [16] . Standard deviations for all measurements are within 3% - 4%.

Diffuse-reflectance spectra of complexes on modified silica surface were registered using a spectrophotometer Specord-40. Samples of adsorbent (0.1 g) with previously adsorbed metals were used for these investigations. Concentration of adsorbed metals was 0.5 - 10 mg per 1 g of a carrier.

Studies of adsorption properties of silicas with chemically bound molecules of guanidine hydrochloride were carried out in the static mode. Sample weight (0.1 g) of modified adsorbent was poured into 25 ml of the solution of salts of the chosen cations and anions with a certain pH (content of metals for Mo(VI), Cr(VI), Zn(II), Cu(II), Cd(II), Co(II) and Pb(II)―100 μg, for V(V)―300 μg, for W(VI)―1 mg) and was kept for 24 h under stirring for determination of a dependence of the adsorption degree on the solution рН. Buffer solutions were added to the working solution in a ratio of 1:5 (5 ml per 25 ml of working solution). Under such conditions depending on the chemical composition of the buffer, the primary coordination spheres of different chemical nature are formed in the initial solutions of transition metal taken for study, where aqua-, amino-, chloride or citrate ligands dominated. The obtained results are presented in Table 1 and Table 2.

Synthesized adsorbent quantitatively removes Zn(II) and Cu(II) cations from distilled water without addition of the buffer solutions. Under these conditions the maximum possible (93% - 97%) extraction of Pb(II), Cd(II) and Co(II) cations is observed. This characteristic of the synthesized chemically modified silica is valuable that would allow extract simultaneously these cations and no additional reagents are required. Also good results for solid-phase extraction of studied ions on the surface of the modified silica are observed in the weakly alkaline medium (pH 8.0), i.e. from initial ammonium complexes.

In the highly acidic media, the obtained adsorbent lost adsorption activity with respect to analyzed cations. Under these conditions, nitrogen atoms of polyhexamethyleneguanidine chloride [17] and of monomeric guanidine hydrochloride are protonated, producing a positive charge on the outside surface of the grafted molecules. As a result, electrostatic repulsion between such positively charged sites and cations is increased and the adsorption value decreases. In the alkaline medium, guanidyl groups are transformed into a deprotonated form and behave as usual amino-containing compounds, which can adsorb cations due to the formation of complexes with nitrogen atoms.

Regularities of adsorption of metal-containing oxoanions by synthesized adsorbent also confirm such behavior. The obtained results show that quantitative extraction of Cr(VI) oxoanions is observed in the acidic medium

(pH 1.7), Mo(VI) and V(V) oxoanions from the weakly acidic solutions, and full removal of W(VI) oxoanions is detected in the acidic (pH 1.0) and weakly acidic media.

Conditions of the kinetic adsorption experiments: weight of adsorbent is 0.1 g, the volume of working solution is 25 ml, metal content in the initial solution is 100 mg (5 mg for W). Results of studies of the kinetic characteristics of the synthesized sorbent with respect to each of investigated ions are summarized in Figure 1.

As seen from the obtained data, the quantitative removal of Cu(II) ions and the maximum possible extraction of Pb(II) ions occur in a relatively short time (10 minutes). At the same time, the practically quantitative adsorption of Cd(II) and Co(II) cations is achieved only for a day. But it is necessary to notice that even for a short time of contact (20 minutes) extraction of the sizable amount of these cations takes place. Thus, the kinetic adsorption characteristics of the obtained adsorbent are similar to the mineral adsorbents.

Adsorption of the major part (80% - 90%) of Cr(VI) and Mo(VI) oxoanions (Figure 1(b)) occurs for a relatively short time (10 - 20 minutes). Unlike these ions, quantitative extraction of V(V) oxoanions is achieved much quicker. A more complicated kinetic dependence was observed for adsorption of W(VI) oxoanions.

Synthesized adsorbent shows much better kinetic properties than silica gel with chemically bound polyhexamethyleneguanidine [18] . Thus, chemisorption of guanidine hydrocloride on the aminosilica surface allows one to improve kinetic characteristics of the silica adsorbent with guanidinium groups in the grafted modifying layer.

For estimation of the adsorption capacity of silicas with chemically bound guanidine the adsorption isotherms of Pb(II), Cd(II), Co(II), Zn(II), Cu(II) cations and Mo(VI)-, W(VI)-, Cr(VI)-, and V(V)-containing anions have been investigated. Experiments were carried out with initial concentration of metals in the solution from 9.6 × 10⁻⁶ up to 3.0 × 10⁻² mol/L. Some of obtained isotherms are represented in Figure 2.

Isotherms of all studied metals belong to the L-type, which may indicate a uniform distribution of ligands on the surface of the synthesized adsorbent. In the case of adsorption of transition metals cations, it provides evidence that the similar complexes with active sites of the modified silica surface are formed for these metals.

The values of adsorption capacity of obtained adsorbent estimated from adsorption isotherms are summarized in Table 3.

Obtained experimental results indicated that adsorption capacity of the silica gel with chemically bound guanidine hydrocloride with respect to metal-containing anions lied at the quite high level inherent to the silica gel with chemically bound guanidine-containing polymers [9] . However, unlike carrier with immobilized polymer, the synthesized adsorbent is characterized by 3 - 7 times higher sorption capacity towards transition metal cations. Essential characteristic of the synthesized modified silica is its ability to quantitatively remove microamounts of studied metal ions.

When studying the adsorption properties of silica with chemically bound guanidine hydrochloride, formation of colored (violet and light blue) complexes of the surface sites with Co(II) and Cu(II) cations, respectively, was detected. Electron diffuse-reflectance spectra of the surface complexes with Co(II) and Cu(II) cations are presented on Figure 3 and Figure 4, respectively.

As known, pink-colored octahedral aqueous complexes [Co(H₂O)₆]²⁺ with absorption in the region of 500 nm are formed in aqueous solutions of Co(II) salts. Such characteristic color was also inherent for the working solutions of Co(II) salts before and during contact with the silica, chemically modified with guanidine hydrochloride. After solid-phase extraction of cobalt ions the light-violet coloration of the adsorbent was observed. Absorption spectra of cobalt compounds, coordinated on the silica surface with chemically bound guanidine hydrochloride, are characterized by three absorbance bands―at λ₁ = 575 nm, λ₂ = 620 - 650 nm and λ₃ = 520 - 530 nm.

According to [19] , the structure of coordinating site for Co(II) ions is changed during binding of these ions with polyhexamethylene guanidine hydrochloride (PHMG) in solution from octahedral, which is characteristic

for aqueous complexes of cobalt [Co(H₂O)₆]²⁺, to tetrahedral corresponding to formation of the complex with [Co(PHMG)₂(H₂O)₂]²⁺ structure (Scheme 2).

Color of the formed compounds, their electronic spectra and literature data [20] - [22] indicate the replacement of aqua-ligands in the primary coordination sphere of Co(II) by nitrogen atoms of grafted molecules guanidine hydrochloride at metal adsorption with formation on the surface the [CoN₂O₂]²⁺ tetrahedral complexes, similar in geometry to coordinating site of complexes, described in [21] .

Existence of a straight-line correlation between the absorbance values of band at λ_max = 640 nm in diffuse reflectance electronic spectra and the amounts of cobalt, adsorbed on the surface of silica gel with chemically bound guanidine hydrochloride (Figure 3(b)), allows to use this dependence for development of adsorption- photometric analysis of microamounts of metal ions.

Diffuse-reflectance electronic spectra of Cu(II) complexes with guanidine are characterized by a maximum absorption at 600 nm (Figure 4(a)), which is typical for square-planar copper complexes. As in case of Co(II), a

Scheme 2. Complexation of Co(II) ions with active sites of surface of the synthesized adsorbent.

straight-line correlation between the absorbance values of band at λ_max = 600 nm and the amounts of copper, adsorbed on the surface of silica gel with chemically bound guanidine hydrochloride, was established (Figure 4(b)). This dependence may be used to develop a quantitative analysis of microamounts of Cu(II) ions in the sorbent phase by photometric method.

The EPR-spectrum of complexes of copper(II) ions with guanidine hydrochloride chemically bound to the silica surface (Figure 5) is characterized by g-anisotropy and hyperfine structure. This indicates that copper ions on the surface of the modified silica are in a divalent state and confirms considerable mobility of the grafted complexing groups. The spectrum has axially symmetric shape with a split of the hyperfine structure of copper nuclei in the parallel orientation (A_|| = 140 × 10⁻⁴ см⁻¹, g_II = 2.308, g_^ = 2.069). Since the anisotropic components of g-factor are in the ratio g_II > g_^ > 2.0, it is possible to affirm that the copper(II) complex has a ground

state, in other words has square shape [23] . The value of g_II is characteristic for four-coordinated Cu(II)

with coordinating site [2N2O]. The coordination takes place through two nitrogen atoms from two ligands and two oxygen atoms from two solvent (water) molecules.