An Enzyme Flow Immunoassay that Uses β-Galactosidase as the Label and a Cellobiose Dehydrogenase Biosensor as the Label Detector
- 22 July 2000
- journal article
- research article
- Published by American Chemical Society (ACS) in Analytical Chemistry
- Vol. 72 (17) , 4171-4177
- https://doi.org/10.1021/ac000128z
Abstract
The aim was to develop a fast generic enzyme flow immunoassay (EFIA) using a beta-galactosidase (beta-GAL) label in combination with colorimetric detection as well as with a new amperometric biosensor as the label detector. The amperometric biosensor was previously developed within the group for the determination of diphenols in surface water samples. Antigen (Ag, analyte), tracer (Ag*, antigen labeled with beta-GAL), and antibody (Ab) were incubated off-line. After the equilibrium was reached, the sample was introduced into the flow system. The antibody complexes, AgAb and Ag*Ab, were trapped in a protein G column while the free unbound tracer was eluted and detected by an amperometric biosensor downstream after substrate reaction. The enzyme label beta-GAL converted the substrate 4-aminophenyl-beta-D-galactopyranoside (4-APG) into 4-aminophenol (4-AP), which subsequently was detected by a cellobiose dehydrogenase (CDH) modified solid graphite electrode. 4-AP was first oxidized at the electrode surface at +300 mV vs Ag/AgCl, and the formed 4-imino quinone (4-IQ) was reduced back to 4-AP by the CDH in the presence of cellobiose. By combining the EFIA with the CDH biosensor, the overall signal of one tracer molecule is amplified at two occasions, i.e., one enzyme label converts the substrate into many 4-AP molecules, and second these are further amplified by the CDH biosensor. The optimum conditions for the EFIA in terms of the molar ratio between tracer and beta-GAL, temperature, flow rate, etc., was investigated with colorimetric detection, using 2-nitrophenyl-beta-D-galactopyranoside (2-NPG) as the beta-GAL substrate. The performance of both the colorimetric and CDH biosensor detection was investigated and both methods were applied for determination of the model compound atrazine in spiked surface water samples. Detection limits of 0.056 +/- 0.008 and 0.038 +/- 0.007 microg L(-1) and IC50 values of 2.04 +/- 0.294 and 0.42 +/- 0.08 microg L(-1) were obtained for colorimetric and CDH detection, respectively. Matrix effects were less pronounced with the CDH biosensor than with colorimetric detection.Keywords
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