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The Impact of Pesticides - Academy Publish

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atmospheric pressure chemical ionisation (APCI) or electrospray ionisation (ESI)are the most commonly used (Granby et al., 2004; Kruve et al., 2011).Regarding sample preparation (Chen et al., 2008; Paíga et al., 2009a, 2009b), ittraditionally involves an extraction with an organic solvent such as include matrixsolid-phase dispersion, solid-phase extraction, supercritical fluid extraction, solidphasemicroextraction, stir bar sorptive extraction and more recently the ‘quick,easy, cheap, effective, rugged, and safe’ (QuECheRS) method (Anastassiades et al.,2003; Wilkowska et al., 2011).Nowadays, several rapid, relatively inexpensive, sensitive screening analyticalbiosensors that need little sample pre-treatment are constantly being developed forthe identification and quantification <strong>of</strong> carbamate compounds (Caetano et al., 2008;Wu et al., 2009; Somerset et al., 2011; Van Dyk and Pletschke, 2011). Biosensorsare based on the intimate contact between a bio-recognition element that interactswith the analyte <strong>of</strong> interest and a transducer element that converts the biorecognitionevent into a measurable signal. Among the different types <strong>of</strong> biosensors,the electrochemical sensors are <strong>of</strong> special interest due to the high sensitivity inherentto the electrochemical detection and the possibility to miniaturize the requiredinstrumentation, thereby making the construction <strong>of</strong> compact and portable analysisdevices possible (Campàs et al., 2009; Somerset et al., 2011). Somerset et al. (2011)reported detection limit <strong>of</strong> 0.880 nmol/L for carbaryl, 0.249 nmol/L for carb<strong>of</strong>uranand 0.111 nmol/L for methomyl using a mercaptobenzothiazole-on-gold biosensorsystem. From the literature reviewed by Van Dyk and Pletschke (2011), the lowerdetection limits are also in the range <strong>of</strong> 0.1 nmol/L (for carb<strong>of</strong>uran, Ciucu et al.,2003) being clear that enzymatic methods, and biosensors, usually are not able toachieve the sensitivity <strong>of</strong> chromatographic methods. However, authors claimed thatthey can serve as a tool for screening <strong>of</strong> hundreds <strong>of</strong> samples in a short period <strong>of</strong>time complementing the existing methods and allowing for a more rapid assessment<strong>of</strong> problematic environments. Each method has unique advantages which cancomplement each other (Rodriguez-Mozaz et al., 2007; Van Dyk and Pletschke,2011).CARBAMATE BIOMARKERSBiomonitoring is defined as the repeated, controlled measurement <strong>of</strong> chemical orbiological markers in fluids, tissues or other accessible samples from subjectsexposed or exposed in the past or to be exposed to chemical, physical or biologicalrisk factors in the workplace and/or the general environment (Manno et al., 2010).Some bioindicators are commonly used since they can reflect the effect <strong>of</strong>contaminants on cellular metabolism and global homeostasis (Tan et al., 2011).González-Fernández et al. (2008) focused on a wide range <strong>of</strong> conventionalbiomarkers and explored a preliminary working scheme for the integration <strong>of</strong> thetriple -omic approach (transcriptomics, proteomics, and metallomics) inenvironmental monitoring. <strong>The</strong>se authors found them useful and a comprehensivealternative in the study <strong>of</strong> environmental issues and the diagnosis <strong>of</strong> contaminationthreats. <strong>The</strong> expansion <strong>of</strong> omic technologies in recent years have contributed to<strong>Academy</strong><strong>Publish</strong>.org - <strong>The</strong> <strong>Impact</strong> <strong>of</strong> <strong>Pesticides</strong>26

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