Mn. Sarrion et al., STRATEGIES FOR THE ANALYSIS OF CHLOROBENZENES IN SOILS USING SOLID-PHASE MICROEXTRACTION COUPLED WITH GAS-CHROMATOGRAPHY ION-TRAP MASS-SPECTROMETRY, Journal of chromatography, 819(1-2), 1998, pp. 197-209
Citations number
29
Categorie Soggetti
Chemistry Analytical","Biochemical Research Methods
Solid-phase microextraction (SPME) was examined as a possible alternat
ive to Soxhlet extraction in the analysis of chlorobenzenes at high co
ncentrations (up to 65 mu g g(-1)) in soils. Gas chromatography-ion tr
ap mass spectrometry (GC-IT-MS) was used and different strategies were
tested in order to obtain suitable responses for chlorobenzenes. Two
headspace SPME methods, using fibres coated with polydimethylsiloxane
(PDMS) as stationary phase, in splitless and split injection modes, re
spectively, and a direct SPME method using 100-mu m PDMS fibre were st
udied. For headspace SPME, 7-mu m and 100-mu m PDMS fibres were used a
nd good sensitivity was obtained by adding 200 mu l of water to the so
il, at a sampling temperature of 30 degrees C and absorption times of
40 and 60 min, respectively. For direct SPME, which involves extractio
n of chlorobenzenes from stirred soil solutions using a 100-mu m PDMS
fibre, the effect of the addition of different organic solvents, such
as methanol or acetone, on the sensitivity and the extraction time was
evaluated. The shortest time to reach equilibrium (50 min) was achiev
ed when a mixture acetone-water (30:70) was added to the sample. Repea
tabilities lower than 8% were obtained for headspace and direct SPME w
ith 100-mu m PDMS fibre, whereas for 7-mu m PDMS fibre, repeatabilitie
s were slightly higher (between 7 and 11%). The SPME methods were appl
ied to the analysis of chlorobenzenes in an industrially contaminated
clay soil, CRM-530, which is a candidate reference material. Chloroben
zenes in this soil were quantified by standard addition, which led to
good reproducibility (R.S.D. between 2 and 10%) for headspace and dire
ct SPME with the 100-mu m PDMS fibre and acceptable detection Limits (
30 to 100 pg g(-1) of soil). The results were consistent with those ob
tained in a European intercomparison exercise. (C) 1998 Elsevier Scien
ce B.V. All rights reserved.