2021
DOI: 10.1016/j.foodchem.2020.128895
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Electrochemical detection of bisphenols in food: A review

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Cited by 76 publications
(16 citation statements)
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“…In the ENCG/HPLC-FLD method, the existence of mNH 2 -MIL-101(Al), β-CD, and GO-based nanohybrids provide the basis for the simultaneous adsorption/extraction of trace pollutants with a wide polarity range; the effervescent reaction speeds up the dispersive process, and the The polarities of pollutants that can be tested are relatively wider; that is to say, both PAHs and BPs can be efficiently extracted simultaneously; (2) The extraction time is shorter (only 40 s); however, it requires 3-5 min [3,41] and even as long as 50 min in the previous reports [39]; (3) in contrast to the MSPE-GC-MS [41], SPME-GC-MS/MS [39], and UHPLC-MS/MS approaches [42], the present method supplies comparable LODs (0.07-0.30 μg kg −1 ) and recov- eries (86.9-103.9%), but it is simple in operation and cheap in the analytical pretreatment cost. Table S3 summarizes the detailed comparisons between the ENCG/HPLC-FLD method with other conventional methods for the determination of PAHs and/or BPs in meat samples [3,[39][40][41][42].…”
Section: Comparison With Previously Reported Methodsmentioning
confidence: 99%
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“…In the ENCG/HPLC-FLD method, the existence of mNH 2 -MIL-101(Al), β-CD, and GO-based nanohybrids provide the basis for the simultaneous adsorption/extraction of trace pollutants with a wide polarity range; the effervescent reaction speeds up the dispersive process, and the The polarities of pollutants that can be tested are relatively wider; that is to say, both PAHs and BPs can be efficiently extracted simultaneously; (2) The extraction time is shorter (only 40 s); however, it requires 3-5 min [3,41] and even as long as 50 min in the previous reports [39]; (3) in contrast to the MSPE-GC-MS [41], SPME-GC-MS/MS [39], and UHPLC-MS/MS approaches [42], the present method supplies comparable LODs (0.07-0.30 μg kg −1 ) and recov- eries (86.9-103.9%), but it is simple in operation and cheap in the analytical pretreatment cost. Table S3 summarizes the detailed comparisons between the ENCG/HPLC-FLD method with other conventional methods for the determination of PAHs and/or BPs in meat samples [3,[39][40][41][42].…”
Section: Comparison With Previously Reported Methodsmentioning
confidence: 99%
“…Polycyclic aromatic hydrocarbons (PAHs) and bisphenolic pollutants (BPs) are two types of ubiquitous pollutants, which possess environmental estrogen effects. PAHs mainly come from incomplete combustion of organic compounds, and several external and internal factors can result in their residues in many kinds of food matrices [1,2]. Especially, the intake of PAHs from all kinds of roasted meat samples is frequent and inevitable.…”
Section: Introductionmentioning
confidence: 99%
“…Due to low concentrations of BPs in samples, various adsorbents have been developed to preconcentrate the BPs with solid phase extraction (SPE) [ 23 ]. Electrochemical detection of bisphenols using modified electrodes (including aptamers or molecularly imprinted polymers) is another popular method [ 24 , 25 ]. These kinds of approaches offer even lower detection limits than the HPLC methods, but they are difficult to transfer for commercial purposes.…”
Section: Introductionmentioning
confidence: 99%
“…The size and shape of the imprints obtained are the same as those of the molecules used as a compound for their preparation. Molecularly imprinted polymers are promising sorbents for separation because they exhibit high affinity and selectivity similar to receptors for target molecules [ 13 , 15 ]. The latest reports from the literature [ 16 , 17 , 18 ] indicate that the molecular imprinting technique is an increasingly developing branch of material engineering that produces materials in various forms, for example, monoliths, membranes, or core-shell sorbents.…”
Section: Introductionmentioning
confidence: 99%
“…Increasingly, reports have appeared that conductive materials of this type are used to detect BPA in food, beverages, or water. In these structures, MIP is an identification element of electrochemical sensors for the detection of Bisphenol A [ 15 , 29 , 30 , 31 , 32 ].…”
Section: Introductionmentioning
confidence: 99%