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The Impact of Pesticides - Academy Publish

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Wang, 2010) and tetracyanoquinodimethane (Martorell et al, 1997) have been usedto reduce the overvoltage <strong>of</strong> oxidation and enhance the sensitivity <strong>of</strong> the detection.<strong>The</strong> ideal biosensor fabrication method should employ mild chemical conditions,allow for large quantities <strong>of</strong> enzyme to be immobilized, provide a favorablemicroenvironment to maintain the enzyme activity, and provide a large surface areafor enzyme-substrate contact within a small total volume. Barriers to mass transport<strong>of</strong> substrate and product should be minimized, and a chemically and mechanicallyrobust system should be provided.Joshi et al (2005) demonstrated a low cost disposable biosensor for the sensitivedetection <strong>of</strong> OP pesticides by using CNTs. A film <strong>of</strong> acid functionalized MWCNTwas cast on the surface <strong>of</strong> the screen-printed electrode by drop drying. <strong>The</strong>n AChEwas immobilized on the CNT film by dropping 10 µL <strong>of</strong> AChE solution and dryingat room temperature under a current <strong>of</strong> air and the electrode was carefully washedwith buffer to remove loosely adsorbed enzyme molecules and bonded CNTs. Todetermine relative inhibition, the AChE-functionalized MWCNT-SPE electrode wasimmersed in a cell containing 2 mL <strong>of</strong> pH 7.4, 50 mM phosphate buffer with 0.1 MKCl under constant stirring. <strong>The</strong> potential was poised at 200 mV (vs. Ag/AgCl).After current stabilization, acetylthiocholine iodide substrate was added to a finalconcentration <strong>of</strong> 1.75 mM. This value <strong>of</strong> current corresponded to I 0 , the currentbefore inhibition. A known concentration <strong>of</strong> paraoxon was then dropped on to theelectrode and incubated for 30 minutes. After incubation, the electrode was washedwith the buffer and the response was measured again as described above, thissecond value corresponded to I i , the current after inhibition. <strong>The</strong> relative inhibition(RI, %) was determined according to the following formula: RI (%) = [(I 0 -I i )/I 0 ]*100 and then related to the inhibitor concentration. <strong>The</strong> biosensor detected aslow as 0.5 nM (0.145 ppb) <strong>of</strong> the paraoxon with good precision, electrode toelectrode reproducibility and stability.Upadhyay et al (2009) have proposed a sensitive amperometric biosensor by usinggold–platinum bimetallic nanoparticles modified glassy carbon electrode for thesensitive detection <strong>of</strong> organophosphate pesticides, carbamates and nerve agent. <strong>The</strong>OP pesticide (paraoxon ethyl), carbamate (aldicarb) and nerve agent (sarin) weredetected by utilizing the unique properties <strong>of</strong> Au–Pt bimetallic NPs, by using thebienzyme (AChE and ChOx) approach .This novel system has been developed byelectrodeposition <strong>of</strong> the Au–Pt bimetallic NPs on the 3-aminopropyltriethoxy silane(3-APTES) modified glassy carbon (GC) electrode. <strong>The</strong>n AChE and ChOx arecoimmobilized on the Au–PtNPs modified electrode by cross-linking enzymes and3-APTES through glutaraldehyde. In this bienzyme system, AChE rapidlyhydrolyzes acetylcholine into acetate and choline. <strong>The</strong> choline is subsequentlyoxidized by ChOx and H 2 O 2 is produced, and finally H 2 O 2 is detectedamperometrically. By using this method paraoxon ethyl, sarin, and aldicarb could bedetected up to 150–200 nM, 40–50 nM, and 40–60 µM respectively at 30–40%inhibition level <strong>of</strong> AChE enzyme and followed linearity in wide range concentration.<strong>Academy</strong><strong>Publish</strong>.org - <strong>The</strong> <strong>Impact</strong> <strong>of</strong> <strong>Pesticides</strong>402

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