RESUMEN
A quantitative risk assessment for exposure to aflatoxin M1 (AFM1) related to the consumption of milk and traditional dairy products of Argentina was developed. The frequency and concentration of AFM1 was modelled at various stages through the milk processes, considering Argentinean practices. Concentration of AFM1 (0.046 µg/l, 95%CI = 0.002-0.264 µg/l) in raw milk was estimated. The AFM1 concentration in milk was sensitive to the carry-over rate (r = 0.80), and milk yield in the first third of lactation during the spring-summer season (r = 0.11). AFB1 levels in silage (r = 0.22), pasture during the spring-summer season (r = 0.11), concentrate (r = 0.08), and cotton seed (r = 0.05) were the factors most correlated with AFM1 concentrations. Although the results showed that MoE values for the mean and median exposure to AFM1 were < 10,000 in infants, toddlers, and other children, the additional cancer risk due to exposure to AFM1 in infants, toddlers, and other children was 0.007, 0.005, and 0.0009 additional cases per year per 100,000 individuals, respectively, which indicates no health concern. In addition, the percentages of the population exceeding HI values (HI > 1) for exposure to AFM1 for infants, toddlers, and other children were 45%, 49.1%, and 40.6%, respectively. Under this scenario, the most susceptible population at risk was children < 10 years old; therefore, it is necessary to establish measures to prevent contamination of AFM1 in milk and milk products.
Asunto(s)
Aflatoxina M1 , Leche , Aflatoxina M1/análisis , Animales , Argentina , Niño , Femenino , Contaminación de Alimentos/análisis , Humanos , Leche/química , Medición de RiesgoRESUMEN
The aim of this study was to assess the risk of exposure to polycyclic aromatic hydrocarbons (PAH) from yerba mate infusions in Uruguay using the margin of exposure approach (MOE) and a probabilistic method (Monte Carlo simulation). Servings/day, portion size, weekly frequency of mate consumption and body weight were the factors considered. The amount in infusions of benz[a]pyrene (B[a]P), PAH2 (sum of chrysene and B[a]P), and PAH4 (sum of benz[a]anthracene, chrysene, benz[b]fluoranthene and B[a]P) were used as markers of PAH exposure. Total content of PAH in infusions had large inter-brand variability (48-54 %) with significant differences among brands. PAH content in infusions prepared as habitually consumed was about 40 % of total content. The probability of occurrence of MOEâ¯<â¯10,000 varied according to the infusion preparation and the marker of exposure used, being higher for infusions prepared for total content and when B[a]P was used as marker of exposure. When the average B[a]P amount in infusion as habitually consumed was used in the simulation model, the probability of MOEâ¯<â¯10,000 was 9 %. The main factors contributing to B[a]P MOE variance were B[a]P amount (28.4 %), servings/day (17.3 %), and portion size (9.6 %). Heavy drinkers of yerba mate with high B[a]P content are those at risk to PAH exposure from mate infusions.
RESUMEN
Maize is a staple food in Mexico that might contain Aflatoxin B1 (AFB1). Nonetheless, data on the exposure and risk assessment of AFB1 from maize for the Mexican population are limited. The aim of the present study was to analyse the occurrence of AFB1 in Mexican nixtamalized maize samples, and to assess the accompanying exposure and risk. Four out of 88 samples contained AFB1 at levels above the limit of detection (1â¯ng/g). AFB1 occurrence values obtained in this study and additional occurrence values from literature were combined with available literature data for mean and P95 consumption of maize based products. For a 70â¯kg body weight person, lower bound and upper bound exposure assessments resulted in estimated daily intakes (EDI) of 0.7-8.5â¯ng/kg bw/day, based on a mean maize consumption. Based on the P95 maize consumption these EDI values amounted to 3.3-11.7â¯ng/kg bw/day. The corresponding Margin of Exposure (MOE) values amounted to 257-20 for the mean and 50-15 for the P95 consumers. The estimated increased cancer risks were 9-320 and 43-439 cases/106 individuals/lifetime of 75 years for the mean and P95 consumers, respectively. Altogether, the assessment reveals the need for continued risk management of AFB1 in Mexico.
RESUMEN
The European Food Safety Authority (EFSA) is developing approaches to cumulative risk assessment of pesticides by assigning individual pesticides to cumulative assessment groups (CAGs). For assignment to CAGs, EFSA recommended to rely on adverse effects on the specific target system. Contractors to EFSA have proposed to allocate individual pesticides into CAGs relying on NOAELs for effects on target organs. This manuscript evaluates the assignments by applying EFSAs criteria to the CAGs "Toxicity to the nervous system" and "Toxicity to the thyroid hormone system (gland or hormones)". Assignment to the CAG "Toxicity to the nervous system" based, for example, on neurochemical effects like choline esterase inhibition is well supported, whereas assignment to the CAG "Toxicity to the thyroid hormone system (gland or hormones)" has been based in the examined case studies on non-reproducible effects seen in single studies or on observations that are not adverse. Therefore, a more detailed effects evaluation is required to assign a pesticide to a CAG for a target organ where many confounders regarding effects are present. Relative potency factors in cumulative risk assessment should be based on benchmark doses from studies in one species with identical study design and human relevance of effects on specific target organs should be analyzed to define minimal margins of exposure.
Asunto(s)
Seguridad de Productos para el Consumidor , Contaminación de Alimentos , Residuos de Plaguicidas/toxicidad , Pruebas de Toxicidad/métodos , Animales , Benchmarking , Factores de Confusión Epidemiológicos , Bases de Datos Factuales , Relación Dosis-Respuesta a Droga , Humanos , Nivel sin Efectos Adversos Observados , Residuos de Plaguicidas/clasificación , Medición de Riesgo , Especificidad de la EspecieRESUMEN
Chloropropanols, including 3-monochloropropane-1,2-diol (3-MCPD) and 1,3-dichloropropan-2-ol (1,3-DCP), comprise a group of chemicalcontaminants with carcinogenic and genotoxic properties. They have been found in a variety of processed foods and food ingredients, suchas hydrolyzed vegetable protein, soy sauce, cereal-based products, malt-derived ingredients, and smoked foods. This study aimed to assessthe dietary exposure to 3-MCPD and 1,3-DCP in Brazil and verify whether the presence of these substances in foods could represent healthrisks. The intake was calculated by combining data on food consumption, provided by the Consumer Expenditure Survey 2008-2009, withthe levels of contaminant occurrence determined by gas chromatography-mass spectrometry. The exposure to 3-MCPD ranged from 0.06 to0.51 µg.kg bw1.day1 considering average and high consumers, while the intake of 1,3-DCP was estimated to be 0.0036 µg.kg bw1.day1 inthe worst case scenario evaluated. Based on these results, it was verified that the Brazilians exposure to chloropropanols does not present asignificant health risk. However, the consumption of specific foods containing high levels of 3-MCPD could exceed the provisional maximumtolerable daily intake of 2 μg.kg bw1 established for this compound and, therefore, represent a potential concern.
Os cloropropanóis, entre eles o 3-monocloropropano-1,2-diol (3-MCPD) e o 1,3-dicloropropan-2-ol (1,3-DCP), compreendem um grupo de contaminantes químicos com propriedades carcinogênicas e genotóxicas, encontrados em diversos alimentos processados e ingredientes alimentícios, como proteína vegetal hidrolisada, molho de soja, produtos à base de cereais, ingredientes derivados de malte e alimentos defumados. Este trabalho teve como objetivo avaliar a exposição ao 3-MCPD e 1,3-DCP pela dieta no Brasil e verificar se a presença destes compostos em alimentos pode representar um risco à saúde da população. A ingestão foi calculada combinando-se dados sobre o consumo alimentar, fornecidos pela Pesquisa de Orçamento Familiares 2008-2009, com os níveis de ocorrência dos contaminantes, determinados por cromatografia gasosa espectrometria de massas. A exposição ao 3-MCPD variou de 0,06 a 0,51 µg.kg pc1.dia1 considerando médios e grandes consumidores, enquanto que a ingestão de 1,3-DCP foi estimada em 0,0036 µg.kg pc1.dia1 no pior cenário avaliado. Com base nesses resultados, verificou-se que a exposição aos cloropropanóis não representa um risco significativo à saúde da população brasileira.Entretanto, o consumo de determinados alimentos contendo altos níveis de 3-MCPD poderia ultrapassar a ingestão diária máxima tolerável provisória de 2 μg.kg pc1 estabelecida para este composto e, assim, representar uma preocupação potencial.