Table 3.
An overview of different electroanalytical techniques, measurement conditions, analytical performance and electrode material used for the determination of bentazone.
Electrode | Technique | Medium | pH | Potential | LOD | Linear Range | Matrix | Reference |
---|---|---|---|---|---|---|---|---|
GCE | FIA/Amperometry | ABS | 4.5 | 1.10 V vs. Ag/AgCl | 1.0 µM | 2.50–50.0 µM | estuarine water | [93] |
MWCNT-IL/RGO/SiC/CILE | Continuous Coulometric FFT CV | 0.05 M PBS | 4.5 | 0.70 V | 0.25 nM | 1.0–150 nM | [88] | |
PANI-β-CD/fMWCNT | CV | PBS | 6 | 0.85 V vs. Ag/AgCl | 1.60 µM | 10.0–80.0 µM | River water | [31] |
PANI-CPE | CV | 0.05 M PBS | 6.9 | [92] | ||||
BDD | DPV | B-R | 4 | 1.07 V vs. Ag/AgCl | 0.50 µM | 2.0–100 µM | River water | [89] |
GCE | DPV | 0.20 M ABS | 3.4 | 0.94 V vs. Ag/AgCl | 10.0 µM | 15.10–2.30 µM | Basagran | [86] |
β-CD-GCE | DPV | 0.10 M BR | 6 | 0.93 V vs. Ag/AgCl | 2.0–14.0 mM | [91] | ||
poly-n-AcMnODEAETPc-GCE | SWV | 0.10 M PBS | 5 | 0.80 V vs. Ag/AgCl | 0.25 µM | 50.0–750 µM | [87] | |
SPE | SWV | 0.10 M PBS | 7 | 0.71 V | 34.0 nM | 0.19–50.0 µM | Ground and lake water | [90] |
Abbreviations: ABS—acetate buffer solution; BDD—boron doped diamond; B-R—Britton-Robinson; CV—cyclic voltammetry; DPV—differential pulse voltammetry; FIA—flow injection analysis; GCE—glassy carbon electrode; LOD—limit of detection; MWCNT-IL/RGO/SiC/CILE—multi-walled carbon nanotube-ionic liquid/reduced graphene/silicone carbide/carbon ionic liquid electrode; PBS—phosphate buffer solution; PANI-β-CD/fMWCNT—polyaniline-β-cyclodextrine/functionalized multi-walled carbon nanotube; PANI-CPE—polyaniline-carbon paste electrode; poly-n-AcMnODEAETPc-GCE—poly-n-manganese acetate octakis-(2-diethyaminoethanethiol)phthalocyanine-glassy carbon electrode; SPE—screen printed electrode; SWV—square wave voltammetry; β-CD-GCE—β-cyclodextrine-glassy carbon electrode.