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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 />

P51 SIMuLTANEOuS SPECIATION OF SELENIuM<br />

AND MERCuRy IN <strong>ENVIRONMENTAL</strong><br />

SAMPLES by uSING A COLuMN SwITChING<br />

SySTEM wITh LIQuID ChROMATOGRAPhy<br />

COuPLED TO ICP-MS<br />

F. MOREnO, T. GARCíA-BARRERA and J. L. GóMEZ-<br />

ARIZA<br />

Departamento de Química y Ciencia de los Materiales “Prof.<br />

J. C. Vílchez Martín”. Facultad de Ciencias Experimentales.<br />

Universidad de Huelva, Campus de El Carmen. 21007<br />

Huelva (Spain),<br />

fernando.moreno@dqcm.uhu.es<br />

Introduction<br />

Mercury is a very toxic element which damages the central<br />

nervous system, endocrine system, kidneys, and other<br />

organs. Exposure over long periods of time or heavy exposure<br />

to mercury vapour can result in brain damage and ultimately<br />

death. Mercury and its compounds can produce serious birth<br />

defects.Compounds of mercury tend to be much more toxic<br />

than the element itself. 1–3<br />

On the other hand selenium is an essential micronutrient<br />

for animals with biological functions as cofactor. However<br />

it is toxic in large doses. Selenium deficiency can lead to<br />

Keshan and Kashin-Beck diseases. If it is taken in excess it<br />

can lead to seleniosis. In addition, several studies have suggested<br />

a link between cancer and selenium deficiency 4 .<br />

It has been issued that Se-methionine inhibits some neurotoxic<br />

effects of methylmercury. 5–7<br />

For this reason, the development of new analytical strategies<br />

for multielemental speciation is a primordial issue.<br />

In the present study, a new method for the detection<br />

of Se- and Hg- species has been developed, including chiral<br />

species.<br />

Experimental<br />

I n s t r u m e n t a t i o n<br />

The HPLC system is an Agilent 1100 series. The<br />

columns used were a Phenomenex Bondclone C18,<br />

300 mm × 3.90 mm, 10 μm; and an Astec Chirobiotic T<br />

column, 250 mm × 4.6 mm.<br />

An inductively coupled plasma mass spectrometer<br />

Model HP 4500 (Hewlett Packard, Yokogawa, Analytical<br />

System, Tokyo, Japan) equipped with a Babington nebuliser<br />

was used in this study.<br />

R e a g e n t s a n d S t a n d a r d s<br />

All reagents were of analytical reagent grade. Deionized<br />

water (18 MΩ cm –1 ) was obtained from a Milli-Q water<br />

purification system (Millipore, UK). 2-mercaptoethanol 98%<br />

was purchased from Sigma–Aldrich (Steinheim, Germany)<br />

and tetraethylammonium chloride from Fluka (Switzerland).<br />

Ammonium acetate and nitric acid were obtained from Merck<br />

(Darmstadt, Germany).<br />

s435<br />

Stock standard solutions of 1,000 mg Se dm –3 were<br />

prepared in deionized water from selenocystine (SeCys 2 ,<br />

Sigma), seleno-DL-methionine (Se-DL-Met, Sigma), seleno-<br />

L-methionine (Se-L-Met, Sigma), selenomethylselenocysteine<br />

(SeMeSeCys, Sigma), selenocystamine (SeCA, Sigma),<br />

sodium selenate (na 2 SeO 4 ) and sodium selenite (na 2 SeO 3 ).<br />

Methylmercury chloride stock standard solution was<br />

prepared at 1,000 mg Hg dm –3 by dissolving methylmercury<br />

chloride (Merck (Darmstadt, Germany) into 2% HnO 3 .<br />

Mercury chloride stock standard solution was prepared as<br />

1,000 mg Hg dm –3 solution by dissolving mercury chloride<br />

(Merck (Darmstadt, Germany) into 10% HnO 3 .<br />

P r o c e d u r e<br />

A 0.075% tetraethylammonium chloride water solution<br />

at pH 4.5 (mobile phase A) and a 5% (v/v) methanol-water<br />

solution containing 0.06 mol dm –3 ammonium acetate and<br />

0.1% (v/v) 2-mercaptoethanol (mobile phase B) were used as<br />

the mobile phases for HPLC. The flow rate was 1 ml min –1 and<br />

the sample injection volume was 100 μl. The columns were<br />

connected using three valves to build a column swithching<br />

system and species were on-line detected by ICP-MS. The<br />

columns outlets were connected directily to the nebulizer of<br />

the ICP-MS system.<br />

Elemental detection was performed using a model 4500<br />

ICP-MS system. The plasma and auxiliary argon flow rates<br />

were 15 and 1 dm 3 min -1 , respectively. The nebulizer gas flow<br />

rate was 1.28 dm 3 min -1 . The forward RF power was fixed at<br />

1,266 W. The dwell time was 3 seconds per isotope and 77 Se,<br />

82 Se and 202 Hg were monitored.<br />

Table I<br />

HPLC conditions<br />

Time Mobile phase Columns<br />

0–5.1 A RP<br />

5.1–6.15 A RP + Chiral<br />

6.15–8.3 A RP<br />

8.3–13.3 A RP + Chiral<br />

13.3–25 B RP<br />

RP = Phenomenex Bondclone C18 column,<br />

300 mm × 3.90 mm, 10 μm<br />

Chiral = Astec Chirobiotic T column, 250 mm × 4.6 mm,<br />

In our study of selenium and mercury speciation have<br />

been successfully separated six selenium compounds and<br />

two major mercury compounds in biological samples using<br />

a reversed-phase column. The chiral species of selenium was<br />

later separated with the second column.<br />

After the injection in the loop, all species go into the<br />

reversed phase column and later directly to the ICP-MS,<br />

using the mobile phase A. With this program, SeCM, SeCys,<br />

SeMeSeCys and Se (IV) elute before 5.1 minutes. At 5.1<br />

minutes we active the second column, and D-selenomethionine<br />

and L-selenomethionine go throught the chiral column.<br />

After that, at 6.15 minutes we switch off the chiral column,

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