Journal of Chromatography A, 1203 (2008) 115–123
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Journal of Chromatography A
journal homepage: www.elsevier.com/locate/chroma
Multi-residue determination of seven quinolones antibiotics in gilthead
seabream using liquid chromatography–tandem mass spectrometry
Victoria Samanidou
a,∗
, Evaggelia Evaggelopoulou
a
, Martin Trötzmüller
b
,
Xinghua Guo
b
, Ernst Lankmayr
b
a
Aristotle University of Thessaloniki, Laboratory of Analytical Chemistry, GR-54124 Thessaloniki, Greece
b
Graz University of Technology, Institute of Analytical Chemistry and Radiochemistry, Technikerstrasse 4, 8010 Graz, Austria
article info
Article history:
Received 9 April 2008
Received in revised form 26 June 2008
Accepted 2 July 2008
Available online 9 July 2008
Keywords:
Quinolones
Fish
Gilthead seabream
LC–MS/MS
Residue analysis
SPE
abstract
A sensitive and selective confirmatory analytical method for the multi-residue determination of seven
quinolones (ciprofloxacin, enrofloxacin, sarafloxacin, danofloxacin, oxolinic acid, nalidixic acid and flume-
quine) in gilthead seabream (Sparus aurata) was developed. The sample pre-treatment involves extraction
with 0.1 M NaOH and purification by solid-phase extraction (SPE) on Waters Oasis HLB cartridges followed
by the determination of all compounds in a single LC–electrospray ionization MS/MS run. Separation was
achieved on a Perfectsil ODS-2, 5 m, 250 mm × 4 mm, analytical column (MZ Analysentechnik) by gra-
dient elution using a mixture of 0.2% (v/v) formic acid, methanol and acetonitrile within 30 min. Multiple
reaction monitoring (MRM) was used for selective detection of each quinolone. Accuracy was evaluated
through recovery studies at three different fortification levels. The mean recoveries are between 90 and
132% for the selected levels with RSD values lower than 20%. The method presents satisfactory results
for linearity, precision and limits of quantification. The latter are much lower than the maximum residue
limits (MRLs) established by the European Union for quinolones in fish tissues (6–8 g/kg).
© 2008 Published by Elsevier B.V.
1. Introduction
The extensive administration of antibiotics in aquaculture has
become a serious problem as their residues can persist in fish
and sea-food. Antibiotics may be directly toxic or be the source of
resistant human pathogens representing a possible risk to human
health. For these reasons regulatory agencies have enacted deci-
sions that keep these substances in aquaculture under control. This
requires monitoring of antibiotic residues [1,2].
Quinolones constitute the main group of antibiotics used both in
human and veterinary medicine for therapeutic purposes as effec-
tive against Gram-negative bacteria. In fish farm industries they
are used for the treatment of the generalized processes of septi-
caemia or of skin diseases. The mechanism of action of quinolones
is bactericidal; in most cases they inhibit the DNA enzyme gyrase of
the bacteria cell, which is indispensable in the duplication of DNA.
However their extensive administration to fish destined for human
consumption, may lead to residues in edible tissues [3–5].
In order to protect human health from the potentially harmful
antibiotic residues, the European Union (EU) has established max-
∗
Corresponding author. Tel.: +30 2310997698; fax: +30 2310997719.
E-mail address: samanidu@chem.auth.gr (V. Samanidou).
imum residue limits (MRLs) for substances authorized for use as
veterinary drugs in food-producing animals (Council Regulation
2377/90/EEC) [6]. Technical guidelines and performance criteria
for residue control, in the framework of the 96/23/EC Directive
[7] are explained in the 657/2002/EC EU Commission Decision [8],
concerning the performance of analytical methods for the determi-
nation of organic residues and contaminants in living animals and
animal products [4].
In literature analytical methods for the determination of
quinolones in fish or sea food are mostly developed for a single
analyte. HPLC is the separation technique of choice with vari-
ous detection techniques: UV detection at 295 nm with limit of
detection (LOD) 0.05 g/g [9], fluorescence detection with LODs
from 1 to 15 g/kg [5,10–15] the LOD values reported were in
the range of 1–15 g/kg as well as chemiluminescence detection
based on the chemiluminescent enhancement by quinolones of
the Ce(SO
4
)
2
–Ru(bpy)
3
2+
–HNO
3
system with LODs from 0.36 to
2.4 g/kg [16].
Other analytical techniques include Capillary electrophoresis
with UV detection (254 nm) [17] or mass spectrometric analysis
with LODs of 20 g/kg [4], as well as an immunochemical-based
multi-residue screening method (enzyme-linked immunosorbent
assay, ELISA) described for fifteen (fluoro)quinolones residues at
levels lower than the established MRLs. The latter cannot identify
0021-9673/$ – see front matter © 2008 Published by Elsevier B.V.
doi:10.1016/j.chroma.2008.07.003