DETERMINATION OF METHYLMERCURY IN BIOLOGICAL SAMPLES AND SEDIMENTS BYCAPILLARY GAS-CHROMATOGRAPHY COUPLED WITH ATOMIC-ABSORPTION SPECTROMETRY AFTER HYDRIDE DERIVATIZATION AND SOLID-PHASE MICROEXTRACTION
B. He et al., DETERMINATION OF METHYLMERCURY IN BIOLOGICAL SAMPLES AND SEDIMENTS BYCAPILLARY GAS-CHROMATOGRAPHY COUPLED WITH ATOMIC-ABSORPTION SPECTROMETRY AFTER HYDRIDE DERIVATIZATION AND SOLID-PHASE MICROEXTRACTION, Journal of analytical atomic spectrometry (Print), 13(10), 1998, pp. 1141-1144
A method for the extraction and determination of methylmercury in biol
ogical samples and sediments by solid phase microextraction (SPME) com
bined with capillary gas chromatography-atomic absorption spectrometry
(GC-AAS) has been proposed. The methylmercury chloride was converted
to its hydride form by potassium tetrahydroborate (KBH4) in a closed h
eadspace vial prior to extraction. A laboratory-assembled SPME device
including a capillary fused-silica fiber and a modified microsyringe w
as used throughout the experiment. The extraction is an equilibrium pr
ocess that depends on the methylmercury hydride partitioning between t
he liquid phase and the fiber. When the equilibrium was reached, the f
iber was directly transferred to a GC column by means of the microsyri
nge, where the analyte was thermally desorbed inside a heated injector
and subsequently the column effluent was atomized by a heated stainle
ss steel tube and detected by an on-line coupled AAS. Several factors
affecting the SPME procedure such as fiber pretreatment with hydrofluo
ric acid, pH buffering, addition of salt and sampling time have been i
nvestigated and optimized. The reproducibility of the SPME procedure w
as 91% and the detection limit based on the signal equal to 3 times th
e baseline noise, was 26 ng. The method was applied to determination o
f methylmercury in biological samples and sediments.