2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures
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Chem. Listy, 102, s265–s1311 (2008) Environmental Chemistry & Technology<br />
P78 SEPARATION AND PRECONCENTRATION<br />
OF ARSENIC, ANTIMONy, SELENIuM AND<br />
TELLuRIuM ON MODIFIED SILICAGELS<br />
FOR ThEIR DETERMINATION by ICP-AES<br />
KRISTýnA URBánKOVá, LUMíR SOMMER and<br />
MARTIn MOOS<br />
Brno University of Technology, Chemistry and Technology of<br />
Environmental Protection,Purkyňova 118, 612 00 Brno,<br />
urbankova@fch.vutbr.cz<br />
Introduction<br />
The determination of toxic or ambivalent microelements<br />
arsenic, antimony, selenium and tellurium in water samples<br />
requires inevitably a preconcentration prior to the determination<br />
by ICP-AES. The separation and preconcentration by<br />
various solid phase extractions were earlier studied and such<br />
technique widely used for water samples. The complexation<br />
of these elements with organic reagents is of particular<br />
interest when interacting with various kinds of silica sorbent<br />
used. 1–5 The combination of organic reagent with cationic<br />
surfactant was examined for sorption in this paper.<br />
Experimental<br />
C h e m i c a l s<br />
All chemicals and solvents used were of analytical grade<br />
quality.<br />
Astasol standards for arsenic, antimony, selenium and<br />
tellurium containing 1.000 ± 0.002 g dm –3 of element were<br />
from Analytica Prague, Czech Republic.<br />
The cationic surfactant 1-ethoxycarbonylpentadecyltrimethylammonium<br />
bromide (Septonex ® ) from Aventa, Czech<br />
Republic and organic reagents 4-(2-Pyridylazo)resorcinol<br />
(PAR), Pyrrollidincarbodithioate (APDC), thiourea (THU)<br />
and 1,2-dihydroxybenzene (PYR) from Lachema, Czech<br />
Republic, diethyldithiocarbamidate (DTC) from Fluka,<br />
Switzerland and 8-hydroxyquinoline-5-sulphonic acid (8-<br />
HQS) from Aldrich, Germany were used.<br />
Modified sorbents were Separon SGX C18, C8, SGX<br />
nH 2 , SGX Cn, SGX RPS and SGX Phenyl with particle size<br />
60 μm, from Tessek Prague, Czech Republic.<br />
I n s t r u m e n t a t i o n<br />
An echelle based ICP-spectrometer with a prism-predisperser<br />
IRIS AP, (Thermo Jarell Ash) and CID detector with<br />
512 × 512 pixels for 195–900 nm, axial plasma discharge of<br />
1.35 kW and echelle grating with 54.4 lines were used.<br />
The following spectral lines [nm] As 228.8, Sb 231.1,<br />
Se 190.6 and Te 214.2 were suitable for final evaluation<br />
only because of their high intensity, selectivity and low background<br />
influences.<br />
s497<br />
Results<br />
S o r p t i o n o f E l e m e n t s o n t h e<br />
S i l i c a S o r b e n t i n t h e P r e s e n c e o f<br />
S u r f a c t a n t<br />
Prior to the sorption, the column was conditioned<br />
successively with 10 ml of distilled water and 10 ml of<br />
5 × 10 –4 – × 10 –2 mol dm –3 aqueous solution of surfactant.<br />
50 ml of solution containing 1 mg dm –3 of As, Sb, Se and<br />
Te (each of them) was always sorbed by a flow rate 1.0–<br />
3.0 ml min –1 at pH 7. The column was then rinsed with 10 ml<br />
of distilled water and the elements eluted with 10 ml of acetone-ethanol<br />
(1 : 1) mixture in the presence of 0.1 mol dm –3<br />
HCl which showed the highest elution efficiency. The organic<br />
eluent was always removed by evaporation under an infra-red<br />
lamp to 1 ml in a suitable Teflon dish.<br />
5 × 10 –3 mol dm –3 Septonex ® is optimal for the retention<br />
of inorganic form of As, Sb, Se and Te. The recovery values<br />
decrease from concentration larger than 1 × 10 –2 mol dm –3<br />
Septonex ® because of the competing influence of micelles<br />
formed under these conditions in solutions. The recovery was<br />
nearly 100 % on SGX C18 (C8) for Sb, Se and Te but for As<br />
it reaches 60 % only. On the other sorbents, the sorption efficiency<br />
decreased. As was retained from 4 % on SGX Phenyl<br />
to 15 % on SGX Cn. 70 % retention of Sb was on SGX nH 2 .<br />
The recoveries for Se were about 90 % for SGX nH 2 , RPS<br />
and Phenyl. On the other hand, more than 40 % of Te was<br />
retained on sorbent SGX RPS and nH 2 .<br />
E f f e c t o f O r g a n i c R e a g e n t s<br />
The retention of monitored microelements was carried<br />
out from 50 ml of solutions containing 1 mg dm –3 of each<br />
metal with organic reagents when the column was previously<br />
conditioned by 5 × 10 –3 mol dm –3 Septonex ® only.<br />
The sorption from solution containing 0.85 × 10 –4 –<br />
3.35 × 10 –4 mol dm –3 PAR was quantitative for Separon<br />
SGX C18, SGX C8, SGX Cn for Sb, Se and Te. On SGX<br />
C18 and C8 the retention of complexes was nearly 100 % for<br />
<strong>2.</strong>77 × 10 –4 –1.1 × 10 –3 mol dm –3 8-HQS and also 6.25 × 10 –4<br />
–8.33 × 10 –3 mol dm –3 PYR. The recoveries about 90 %<br />
were observed for 4.86 × 10 –4 –7.29 × 10 –4 mol dm –3 APDC<br />
and about 80 % for 4.90 × 10 –4 –1.50 × 10 –3 mol dm –3 DTC<br />
or 1.05 × 10 –3 –4.20 × 10 –3 mol dm –3 THU for Sb, Se and<br />
Te. The sorption of As was far from being quantitative.<br />
1.70 × 10 –4 mol dm –3 PAR can be used for the retention of As,<br />
Sb, Te on SGX nH 2 and SGX RPS for As, Sb, Se. On the<br />
other hand, <strong>2.</strong>77 × 10 –4 mol dm –3 8-HQS is optimal for Se on<br />
SGX nH 2 and SGX Phenyl and <strong>2.</strong>43 × 10 –4 mol dm –3 DTC<br />
was suitable for the retention of Te on SGX RPS, SGX Phenyl<br />
and for As on SGX Phenyl.<br />
E f f e c t o f S a m p l e V o l u m e<br />
The influence of sample volume was tested for the retention<br />
from 50–1,000 ml solution containing 0.2–0.01 mg dm –3<br />
each of element in the presence of the particular organic reagents<br />
after conditioning. This corresponds to a 5–100-fold