Abstract

Background: This study aimed to prepare monoclonal antibodies (mAbs) with high immunoreactivity, sensitivity, and specificity for the chelate (Cr(III)-EDTA) of trivalent chromium ion (Cr(III)) and ethylenediamine tetraacetic acid (EDTA). Further, the study established an indirect competitive enzyme-linked immunosorbent assay (icELISA) for detecting the total chromium content in food, feed, and environmental samples. Methods: Hapten Cr(III)-iEDTA was synthesized by chelating Cr(III) with isothiocyanatebenzyl-EDTA (iEDTA). Immunogen Cr(III)-iEDTA-BSA formed by chelating Cr(III)-iEDTA with bovine serum albumin (BSA), and coating antigen Cr(III)-iEDTA-OVA formed by chelating Cr(III)-iEDTA with ovalbumin (OVA) were prepared using the isothiocyanate method and identified by ultraviolet spectra (UV) and inductively coupled plasma optical emission spectrometry (ICP-OES). Balb/c mice were immunized with the Cr(III)-iEDTA-BSA, and the anti Cr(III)-EDTA mAb cell lines were screened by cell fusion. The Cr(III)-EDTA mAbs were prepared by induced ascites in vivo, and their immunological characteristics were assessed. Results: The immunogen Cr(III)-iEDTA-BSA was successfully synthesized, and the molecular binding ratio of Cr(III) to BSA was 15.48:1. Three hybridoma cell lines 2A3, 2A11, and 3D9 were screened, among which 2A3 was the best cell line. The 2A3 secreted antibody was stable after six passages, the affinity constant (Ka) was 2.69 × 109 L/mol, its 50% inhibition concentration (IC50) of Cr(III)-EDTA was 8.64 μg/L, and it had no cross-reactivity (CR%) with other heavy metal ion chelates except for a slight CR with Fe(III)-EDTA (1.12%). An icELISA detection method for Cr(III)-EDTA was established, with a limit of detection (LOD) of 1.0 μg/L and a working range of 1.13 to 66.30 μg/L. The average spiked recovery intra-assay rates were 90% to 109.5%, while the average recovery inter-assay rates were 90.4% to 97.2%. The intra-and inter-assay coefficient of variations (CVs) were 11.5% to 12.6% and 11.1% to 12.7%, respectively. The preliminary application of the icELISA and the comparison with ICP-OES showed that the coincidence rate of the two methods was 100%, and the correlation coefficient was 0.987. Conclusions: The study successfully established an icELISA method that meets the requirements for detecting the Cr(III)-EDTA chelate content in food, feed, and environmental samples, based on Cr(III)-EDTA mAb, and carried out its preliminary practical application.

Highlights

  • Licensee MDPI, Basel, Switzerland.Heavy metal chromium (Cr) is an important modern industrial strategic resource widely used in metallurgy, fire resistance, chemical industry, national defense, and other fields

  • The results indicated that the immunogen synthesis and Cr(III)-iEDTA (Figure 1)

  • The results showed that with the continuous strength, the Amax/IC50 gradually decreased while the IC50 value gradually increased, increase in ionic strength, the Amax/IC50 gradually decreased while the IC50 value gradi.e., the sensitivity of indirect competitive enzyme-linked immunosorbent assay (icELISA) decreased

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Summary

Introduction

Licensee MDPI, Basel, Switzerland.Heavy metal chromium (Cr) is an important modern industrial strategic resource widely used in metallurgy, fire resistance, chemical industry, national defense, and other fields. The metal has become a serious pollutant in the environment and food due to excessive use and a lack of corresponding protection measures [1]. Based on the analysis of 1625 sites and 1799 literatures, Li et al [2] reported a nationwide assessment of Cr pollution in agricultural soils in China for the first time. The Cr levels exceeded the standard by 65 times, which once again aroused the widespread concern of the government and society about excessive Cr pollution. In order to strictly control Cr pollution in food, the United States Environmental Protection Agency (EPA), the World Health Organization (WHO) and the European Community (EC) set the maximum limit of Cr in drinking water to 100 μg/L (EPA 822-R-06-013), 50 μg/L (WHO ISBN 9241546743) and 50 μg/L (98/83/EC), respectively [11]. The Chinese national standard (GB 2762-2017 National Food Safety Standard-Limits of Contaminants in Food) stipulates that the maximum Cr limit should be less than 2.0 mg/kg, 1.0 mg/kg and

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