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PDF file - Facultatea de Chimie şi Inginerie Chimică

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HEAVY METAL IONS REMOVAL FROM MODEL WASTEWATERS USING ORAŞUL NOU<br />

as follows: 3631.30 cm -1 – stretching vibrations of isolate hydroxyls and OH<br />

less firmly bond to the tetrahedrical outer layer, 3448.10 cm -1 – stretching<br />

vibrations of the structural OH and also of the hydration water, 1639.20 cm -1 –<br />

angular <strong>de</strong>formation of hydroxyls from adsorbed water molecules (held in<br />

interlayers), 1095.37 and 1047.53 cm -1 – main bands corresponding to the<br />

stretching vibrations of Si,Al-O, 794.53 and a shoul<strong>de</strong>r at 620.97cm -1 – weak<br />

bands corresponding to the stretching vibrations of Si,Al-O (there are not specific<br />

peaks for montmorillonite and could be attributed to the accompanying minerals),<br />

and 474.40 and 524.54 cm -1 bending vibrations of Si-O-M bonds (M can be<br />

Mg, Al, Fe).<br />

Absorbance<br />

1.8<br />

1.6<br />

1.4<br />

1.2<br />

1<br />

0.8<br />

0.6<br />

0.4<br />

0.2<br />

474.40<br />

794.53<br />

1095.37<br />

1400.07<br />

1639.20<br />

3448.10<br />

3631.30<br />

0<br />

400 900 1400 1900 2400 2900 3400 3900<br />

Wavenumber, [cm -1 ]<br />

Figure 2. FTIR spectrum of the bentonite sample from Oraşul Nou <strong>de</strong>posit.<br />

Heavy metal ions removal results<br />

The results obtained in case of zinc removal from monocomponent<br />

mo<strong>de</strong>l solutions are presented and discussed in terms of removal efficiency<br />

and adsorption capacity.<br />

In figure 3, evolution of zinc removal efficiency in time is presented<br />

for the experiment conducted in static regime (Ci = 125 mg Zn<br />

131<br />

2+ /L, 2 g<br />

bentonite, 20 ml zinc solution). A closer inspection of this evolution led to<br />

the conclusion that in the first 24 hours, concentration of zinc ions drops<br />

significantly from the initial value to 1.68 mg Zn 2+ /L, leading to high removal<br />

efficiency (98.71%). Equilibrium was reached in 48 hours, when concentration<br />

of zinc ions in solution drops to 0 (100% efficiency) and adsorption capacity<br />

increased up to 1.3003 mg Zn 2+ /g bentonite.<br />

The experiments realised in dynamic regime (3D shaker) were conducted<br />

with the modification of the initial concentration of zinc in mo<strong>de</strong>l solutions,<br />

and bentonite quantity. Results are presented in figures 4 to 7 in terms of<br />

removal efficiency and adsorption capacity.

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