Environmental Engineering Reference
In-Depth Information
of the GC × GC coupling to MS has been shown in the simultaneous determination of 97
environmental contaminants, including pesticides at ng/L levels (Matamoros et al. 2010).
Recently, one of the hottest trends in water contaminant analysis has been the use of
LC with full scan and high-resolution MS (HRMS) to identify unknown contaminants
(nontarget analysis) or provide confirmation data (Richardson 2009). This identification
relies on the mass accuracy obtained, with mass errors below 2 mDa or 5 ppm normally
being accepted for a positive identification (Hernández et al. 2004). Nowadays, the most
commonly used mass analyzer in HRMS instruments is TOF. For example, it has been
shown that the higher mass resolution of TOF allows the detection of some pesticides in
river water, even when they are accompanied by isobaric compounds (Hogenboom et al.
1999). Furthermore, LC-TOF has been the selected technique for the determination of pes-
ticide degradation products in environmental, biological, and food matrices (Martínez
Vidal et al. 2009). Even more useful in terms of confirmatory analysis is a quadrupole-TOF
hybrid instrument (Q-TOF) as it allows MS 2 experiments to be performed, thus improv-
ing selectivity (Hernández et al. 2004; Barceló and Petrovic 2007). LC-Q-TOF has been
successfully applied in the nontarget analysis of pesticides (Meng et al. 2010) and their
metabolites (Hernández et al. 2008a) as well as disinfection by-products (Brix et al. 2009).
Acknowledgments
The authors greatly appreciate the financial support from the Ministry of Science and
Technological Development of the Republic of Serbia (Project No. 172007).
References
Acero, J. L., Benitez, F. J., Real, F. J., and Gonzalez, M. 2008. Chlorination of organophosphorus pesti-
cides in natural waters. J. Hazard. Mater. 153: 320-328.
Alder, L., Greulich, K., Kempe, G., and Vieth, B. 2006. Residue analysis of 500 high priority pesticides:
Better by GC-MS or LC-MS/MS? Mass Spectrom. Rev. 25: 838-865.
Anshup, T. P. 2009. Noble metal nanoparticles for water purification: A critical review. Thin Solid
Films 517: 6441-6478.
Asperger, A., Efer, J., Koal, T., and Engewald, W. 2002. Trace determination of priority pesticides in
water by means of high-speed on-line solid-phase extraction-liquid chromatography-tandem
mass spectrometry using turbulent-flow chromatography columns for enrichment and a short
monolithic column for fast liquid chromatographic separation. J. Chromatogr. A 960: 109-119.
Ayranci, E. and Hoda, N. 2004. Studies on removal of metribuzin, bromacil, 2,4-D and atrazine from
water by adsorption on high area carbon cloth. J. Hazard. Mater. 112: 163-168.
Bach, M., Huber, A., and Frede, H.-G. 2001. Input pathways and river load of pesticides in
Germany - A national scale modeling assessment. Water Sci. Technol. 43: 261-268.
Bach, M., Letzel, M., and Kaul, U., et al. 2010. Measurement and modeling of bentazone in the river
Main (Germany) originating from point and non-point sources. Water Res. 44: 3725-3733.
Bachman, J. and Patterson, H. H. 1999. Photodecomposition of the carbamate pesticide carbofuran:
Kinetics and the influence of dissolved organic matter. Environ. Sci. Technol. 33: 874-881.
Baćić-Vukčević, M., Udovičić, A., Laušević, Z., Perić-Grujić, A., and Laušević, M. 2006. Surface char-
acteristics and modification of different carbon materials. Mater. Sci. Forum 518: 217-222.
 
Search WWH ::




Custom Search