Abstract

Ochratoxin A is a nephrotoxic and renal carcinogenic mycotoxin and is a common contaminant of various food commodities. Eighty six kinds of foodstuffs (1032 food samples) were collected in 2011–2013. High-performance liquid chromatography with fluorescence detection was used for ochratoxin A determination. Limit of quantification of the method varied between 0.01–0.2 μg/kg depending on the food matrices. The most exposed population is children aged 4–6 years old. Globally for this group, the maximum ochratoxin A dietary exposure for “average consumer” was estimated at 3.3 ng/kg bw/day (lower bound, considering the analytical values below the limit of quantification as 0) and 3.9 ng/kg bw/day (middle bound, considering the analytical values below the limit of quantification as 1/2 limit of quantification). Important sources of exposure for this latter group include grain-based products, confectionery, meat products and fruit juice. The dietary intake for “high consumers” in the group 4–6 years old was estimated from grains and grain-based products at 19.8 ng/kg bw/day (middle bound), from tea at 12.0 ng/kg bw/day (middle bound) and from confectionery at 6.5 ng/kg bw/day (middle bound). For men aged 18–59 years old beer was the main contributor with an intake of 2.60 ng/kg bw/day (“high consumers”, middle bound). Tea and grain-based products were identified to be the main contributors for dietary exposure in women aged 18–59 years old. Coffee and wine were identified as a higher contributor of the OTA intake in the population group of women aged 18–59 years old compared to the other population groups.

Highlights

  • Ochratoxin A (OTA) is a nephrotoxic and renal carcinogenic mycotoxin [1,2,3]

  • The current paper aims to present the data on the dietary exposure assessment of OTA with respect to 10 sex-age groups in the Czech Republic (CR) as investigated in the research project

  • A difficult step in the dietary exposure assessment is how to handle data on concentrations reported below the limit of quantification (LOQ) but over the limit of detection (LOD)

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Summary

Introduction

OTA is produced by Aspergillus and Penicillium species [4,5,6,7] and is a common contaminant of various foodstuffs of plant and animal origin including cereals, spices, coffee, cacao, beer, wine, raisins, pulses, meat, meat products, or edible offal [7]. Considering such ubiquity and the mentioned toxic effects, international authorities have proposed tolerable daily or weekly intakes for OTA, which indicate the dose that can be safely consumed daily/weekly over a lifetime without incurring any appreciable adverse health effects. TWI was established on the basis of the lowest observed adverse effect level (LOAEL) of 8 μg/kg bw/day for early markers of renal toxicity in pigs (the most sensitive animal species), and applying a composite uncertainty factor of 450 for the uncertainties in the extrapolation of experimental data derived from animals to humans as well as for intra-species variability [8].

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