Page 366 - Multidimensional Chromatography
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Multidimensional Chromatography in Environmental Analysis       357

                              A general step is the coupling of a 10 mm long precolumn (2–3 mm i.d.), filled
                           with C 18 or polystyrene–divinylbenzene, to a 10–50  m RPLC column. A PLRP-s
                           precolumn achieved higher breakthrough volume for the more polar compounds and
                           is thus highly recommended. This set-up has been used to determine several groups
                           of pesticides (40, 55–62), phenols (41, 63–65), PAHs (66, 67), naphthalenesul-
                           fonates (68, 69), etc. The sample volume depends on the breakthrough volumes of
                           the compounds to be determined, with typical values being between 10 and 200 ml.
                              For example, Figure 13.13 shows the chromatogram obtained when 200 ml of tap
                           water was spiked at levels of 1 g l  1  of such pesticides. The limits of detection
                                                                             1
                           achieved by using this method were between 0.05 and 0.5  g l , although more polar
                           compounds such as vamidothion or 4-nitrophenol could not be determined (61).
                              Various highly crosslinked polymers, with slightly different properties, such as
                           Envi-Chrom P, Lichrolut EN, Isolute ENV or  HYSphere-1, have been applied in
                           environmental analysis, mainly for polar compounds. For phenol, for instance,
                           which is a polar compound, the recoveries (%) when 100 ml of sample was analysed
                           were 5, 16 and 6 for PLRP-s, Envi-Chrom P and Lichrolut EN, respectively (70).
                              Chemically modified polymers have been used to determine polar compounds in
                           water samples (37, 71). Chemical modification involves introducing a polar group
                           into polymeric resins. These give higher recoveries than their unmodified analogues
                           for polar analytes. This is due to an increase in surface polarity which enables the
                           aqueous sample to make better contact with the surface of the resin (35).



























                           Figure 13.13 On-line trace enrichment–RPLC-diode-array detection (DAD) chromatogram
                           (at 230 nm) obtained from 200 ml of tap water spiked with various pesticides at levels of 1  g
                             1
                           l . Reprinted from Chromatographia, 43, C. Aguilar et al., ‘Determination of pesticides by
                           on-line trace enrichment–reversed-phase liquid chromatography–diode-array detection and
                           confirmation by particle-beam mass spectrometry’, pp. 592–598, 1996, with permission from
                           Vieweg Publishing.
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