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 />
enrichment of As, Sb, Se and Te which enables the final use<br />
of ICP-AES.<br />
Volumes of up to 1,000 ml have no effect on the retention<br />
efficiency on Separon SGX C18, C8 and SGX RPS.<br />
The sorption is however quantitative from 500 ml only on<br />
SGX nH 2 , SGX Cn and SGX Phenyl. The weakening of the<br />
retention forces of ionic associate or complexes on the surface<br />
of sorbent may supports the subsequent washing out of<br />
the element species from the column.<br />
A p p l i c a t i o n f o r W a t e r S a m p l e s o n<br />
S e p a r o n S G X C 1 8<br />
Standards of folowing elements were spiked to equilibrated<br />
drinking, mineral and river water samples containing<br />
no detectable amounts of these elements. The Separon SGX<br />
C18 was previously conditioned by 10 ml of distilled water<br />
and 10 ml of 5 × 10 –3 mol dm –3 Septonex ® . The sorption was<br />
provided from 250 ml of sample solutions in the presence of<br />
1.68 × 10 –4 mol dm –3 PAR. Conclusions<br />
Table I<br />
The recovery (%) of arsenic and antimony in water samples a<br />
Spikes<br />
[mg dm<br />
c b<br />
element Arsenic Antimony<br />
–3 ] [mg dm –3 ]<br />
Mineral water<br />
0.25 0.01 58.30 ± <strong>2.</strong>44 98.74 ± <strong>2.</strong>70<br />
0.50 0.02 60.02 ± <strong>2.</strong>60 101.3 ± 3.40<br />
1.00 0.04 60.23 ± 3.36<br />
River water<br />
99.54 ± <strong>2.</strong>87<br />
0.25 0.01 59.71 ± 3.14 100.9 ± <strong>2.</strong>39<br />
0.50 0.02 60.90 ± <strong>2.</strong>69 97.26 ± 3.53<br />
1.00 0.04 6<strong>2.</strong>34 ± <strong>2.</strong>43 100.9 ± 3.09<br />
aThe analysis was carried out in triplicate and evaluated<br />
according Dean and Dixon6 bConcentration in 250 ml of water sample<br />
s498<br />
Table II<br />
The recovery (%) of selenium and tellurium in water samples<br />
a<br />
Spikes c element b<br />
Selenium Tellurium<br />
[mg dm –3 ] [mg dm –3 ]<br />
Mineral water<br />
0.25 0.01 100.5 ± <strong>2.</strong>57 100.5 ± 3.06<br />
0.50 0.02 98.60 ± 3.00 99.50 ± 3.07<br />
1.00 0.04 99.23 ± <strong>2.</strong>66 99.78 ± <strong>2.</strong>33<br />
River water<br />
0.25 0.01 99.78 ± <strong>2.</strong>71 100.8 ± <strong>2.</strong>35<br />
0.50 0.02 98.90 ± <strong>2.</strong>80 99.64 ± <strong>2.</strong>47<br />
1.00 0.04 101.7 ± <strong>2.</strong>11 100.2 ± 1.73<br />
a The analysis was carried out in triplicate and evaluated according<br />
Dean and Dixon 6<br />
b Concentration in 250 ml of water sample<br />
The separation and preconcentration of arsenic,<br />
antimony, selenium and tellurium in the presence of<br />
1.68 × 10 –4 mol dm –3 4-(2-Pyridylazo) resorcinol after previous<br />
conditioning with 5 × 10 –3 mol dm –3 Septonex ® was<br />
described in this paper. This procedure was successfully used<br />
for determination of these elements by ICP-AES in real water<br />
samples.<br />
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