Page 354 - Multidimensional Chromatography
P. 354

Multidimensional Chromatography in Environmental Analysis       345

                              Depending on the kind of sorbent in the precolumn connected on-line to the
                           analytical column, the retention of analytes in the precolumn may be more or less
                           selective.
                              The sorbents that are most frequently used in environmental analysis are
                           C 18 -silica based sorbents, polymeric sorbents (usually styrenedivinilbenzene) and
                           graphitized carbon. In order to increase the selectivity of these sorbents, immunosor-
                           bents (35, 36)  have been developed and used with good results, while recently,
                           molecularly imprinted polymers have started be to used (35, 36).
                              Polar compounds present the most problems because of their low breakthrough
                           volumes with common sorbents. In the last few years, highly crosslinked polymers
                           have become commercially available which involve higher retention capacities for
                           the more polar analytes (37, 38). Polymers have also been chemically modified with
                           polar groups in order to increase the retention of the compounds previously
                           mentioned (35, 37).
                              Instead of a sorbent contained in a precolumn, discs can also be used with a spe-
                           cial device (38, 39) which enables the number of discs to be changed easily, although
                           this technique is currently limited to the kind of discs that are commercially
                           available.
                              The characteristics of the sorbent in the precolumn may lead to problems when
                           coupling the two systems. Therefore, when the analytes are more retained in the pre-
                           column than in the analytical column, peak broadening may appear, even when the
                           analytes are eluted in the backflush mode (40). This has been solved with a special
                           design in which the analytes retained in the precolumn are eluted with only the
                           organic solvent of the mobile phase and the corresponding mobile phase is subse-
                           quently formed (40, 41).
                              On-line SPE–LC has been widely used in environmental analysis to solve the
                           problems caused by the low concentrations of the analytes to be detected and also to
                           automate the analysis (42–44).


                           13.3.2  EXAMPLES OF MULTIDIMENSIONAL LIQUID
                           CHROMATOGRAPHY IN ENVIRONMENTAL ANALYSIS

                           LC–LC is applied to environmental samples with two major aims, i.e. to determine a
                           single analyte and to determine a group of analytes (by the multiresidue methods) at
                           the low levels required by legislation in both cases. Some examples of these are dis-
                           cussed below. In addition, some applications for the particular case of SPE–LC, will
                           also be described.
                              The single-residue methodology has been used to determine analytes with differ-
                           ent characteristics. The main advantage of this technique is the short analysis time.
                           LC–LC methodology has been applied to various polar analytes, such as bentazone
                           (46), and less polar compounds such as isoproturon (46) or pentaclorphenol (47).
                           Most applications refer to water samples (46, 48), although solid samples have also
                           been studied (31, 49, 50). Soil samples contain more interfering compounds so
                           clean-up is even more important when analysing soil extracts. Coupled  RPLC is
   349   350   351   352   353   354   355   356   357   358   359