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1.
Arch Toxicol ; 93(12): 3503-3521, 2019 12.
Article in English | MEDLINE | ID: mdl-31659427

ABSTRACT

Aluminium is one of the most abundant elements in earth's crust and its manifold uses result in an exposure of the population from many sources. Developmental toxicity, effects on the urinary tract and neurotoxicity are known effects of aluminium and its compounds. Here, we assessed the health risks resulting from total consumer exposure towards aluminium and various aluminium compounds, including contributions from foodstuffs, food additives, food contact materials (FCM), and cosmetic products. For the estimation of aluminium contents in foodstuff, data from the German "Pilot-Total-Diet-Study" were used, which was conducted as part of the European TDS-Exposure project. These were combined with consumption data from the German National Consumption Survey II to yield aluminium exposure via food for adults. It was found that the average weekly aluminium exposure resulting from food intake amounts to approx. 50% of the tolerable weekly intake (TWI) of 1 mg/kg body weight (bw)/week, derived by the European Food Safety Authority (EFSA). For children, data from the French "Infant Total Diet Study" and the "Second French Total Diet Study" were used to estimate aluminium exposure via food. As a result, the TWI can be exhausted or slightly exceeded-particularly for infants who are not exclusively breastfed and young children relying on specially adapted diets (e.g. soy-based, lactose free, hypoallergenic). When taking into account the overall aluminium exposure from foods, cosmetic products (cosmetics), pharmaceuticals and FCM from uncoated aluminium, a significant exceedance of the EFSA-derived TWI and even the PTWI of 2 mg/kg bw/week, derived by the Joint FAO/WHO Expert Committee on Food Additives, may occur. Specifically, high exposure levels were found for adolescents aged 11-14 years. Although exposure data were collected with special regard to the German population, it is also representative for European and comparable to international consumers. From a toxicological point of view, regular exceedance of the lifetime tolerable aluminium intake (TWI/PTWI) is undesirable, since this results in an increased risk for health impairments. Consequently, recommendations on how to reduce overall aluminium exposure are given.


Subject(s)
Aluminum/toxicity , Environmental Exposure/adverse effects , Risk Assessment/methods , Adolescent , Aluminum/pharmacokinetics , Animals , Carcinogens/toxicity , Child , Child, Preschool , Dietary Exposure/adverse effects , Dietary Exposure/analysis , Environmental Exposure/analysis , Food Additives/adverse effects , Food Contamination/analysis , Humans , Infant , Mutagens/toxicity , Toxicity Tests, Acute
3.
Article in German | MEDLINE | ID: mdl-28573516

ABSTRACT

Environmental emissions of organic contaminants are caused by man-made and natural combustion processes, industrial production facilities, and the release from products. Food represents the main source of human exposure for some of these compounds. This is the case for three groups of persistent organic contaminants: (1) per- and polyfluoroalkyl substances (PFAS), (2) polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs), polychlorinated biphenyls (PCBs), and for (3) polycyclic aromatic hydrocarbons (PAHs). The issues regarding PCDD/F emissions were already recognized as a problem in the 1970s and have since then been effectively regulated; the impact of PFAS as global anthropogenic environmental contaminants was identified much later.A system of toxicity equivalency factors (TEF system) was established for the assessment of the toxic potency of a mixed exposure to PCDD/F and certain PCBs. For the health assessment and regulation of PAHs and PFAS, no such system has been implemented so far. For PFAS, a re-evaluation of the present tolerable daily intake values (TDI values) is currently being discussed, as new insights into toxicology and epidemiology have been gained.The persistence in the environment of the compound groups discussed here leads to entry into the food chain over long periods of time, even if access into the environment is minimized. This requires a long-term continuation of the monitoring of food stuffs and forward-looking risk assessment approaches and regulatory measures.


Subject(s)
Environmental Exposure/adverse effects , Environmental Exposure/analysis , Food Contamination/analysis , Food Contamination/prevention & control , Organic Chemicals/adverse effects , Organic Chemicals/analysis , Germany , Risk Factors , Toxicity Tests
4.
Arch Toxicol ; 89(6): 823-50, 2015 Jun.
Article in English | MEDLINE | ID: mdl-25820917

ABSTRACT

The advent of new testing systems and "omics"-technologies has left regulatory toxicology facing one of the biggest challenges for decades. That is the question whether and how these methods can be used for regulatory purposes. The new methods undoubtedly enable regulators to address important open questions of toxicology such as species-specific toxicity, mixture toxicity, low-dose effects, endocrine effects or nanotoxicology, while promising faster and more efficient toxicity testing with the use of less animals. Consequently, the respective assays, methods and testing strategies are subject of several research programs worldwide. On the other hand, the practical application of such tests for regulatory purposes is a matter of ongoing debate. This document summarizes key aspects of this debate in the light of the European "regulatory status quo", while elucidating new perspectives for regulatory toxicity testing.


Subject(s)
Animal Testing Alternatives/methods , Toxicity Tests/methods , Toxicology/methods , Animal Testing Alternatives/legislation & jurisprudence , Animals , Europe , Government Regulation , Humans , Species Specificity , Toxicity Tests/standards , Toxicity Tests/trends , Toxicology/legislation & jurisprudence , Toxicology/standards , Toxicology/trends , United States
5.
Mol Nutr Food Res ; 53(4): 500-7, 2009 Apr.
Article in English | MEDLINE | ID: mdl-19360756

ABSTRACT

As a basis for the collection of occurrence and exposure data of ergot alkaloids in food, an HPLC method coupled with fluorimetric detection (HPLC-FLD) for the determination of 12 pharmacologically active ergot alkaloids in rye and rye products was developed. Samples were extracted with a mixture of ethyl acetate, methanol, and aqueous ammonia, followed by centrifugation and purification by solid phase filtration (SPF) with basic alumina. After solvent adjustment, the samples were analyzed by HPLC-FLD using a phenyl-hexyl-column. Recoveries for five major alkaloids were between 89.3% (ergotamine) and 99.8% (alpha-ergokryptine) with a maximum LOQ of 3.3 microg/kg (ergometrine). Precision expressed as RSD ranged from 2.8% (ergocristine) to 12.4% (alpha-ergokryptine) for repeatability, and from 6.5% (ergocornine) to 14.9% (ergotamine) for within-laboratory reproducibility, respectively. In a survey of 39 rye product samples, ergocristine and ergotamine were found to be the major alkaloids in commercially available rye products with contents of 127 microg/kg (ergocristine), and 134 microg/kg (ergotamine) in rye flour, and 152.5 and 117.8 microg/kg in coarse meal, respectively.


Subject(s)
Chromatography, High Pressure Liquid/methods , Ergot Alkaloids/analysis , Risk Assessment , Secale/microbiology , Flour/analysis , Flour/microbiology , Fluorometry , Secale/chemistry
6.
Toxicol Lett ; 175(1-3): 118-35, 2007 Dec 10.
Article in English | MEDLINE | ID: mdl-18024010

ABSTRACT

A number of zero tolerance provisions are contained in both food and animal feed law, e.g. for chemical substances whose occurrence is not permitted or is directly prohibited in food or animal feed. In the European Union, bans of this kind were introduced to give consumers and animals the greatest possible protection from substances with a possible hazard potential within the intendment of the hazard prevention principles and current precautionary measures. This also applies to substances for which an acceptable daily intake cannot be derived and a maximum residue limit cannot, therefore, be established, e.g. due to missing or inadequate toxicological data. Zero tolerances are also under discussion as trade barriers because their use has triggered numerous legal disputes. This paper draws together the results of an evaluation of alternative risk assessment methods to be used for the risk assessment of substances to which currently only zero tolerances apply. It will demonstrate that, depending on the available toxicological data, a scientifically sound risk assessment may still be possible. In this context, the two concepts - margin of exposure and threshold of toxicological concern - are very promising approaches. Until the scientific and sociopolitical discussions have been completed, it is essential that the principle of zero tolerances be upheld, especially for those substances which may be genotoxic carcinogens. In microbiology, there is no legal room for manoeuvre with regard to food safety criteria established for reasons of consumer health protection on the basis of scientific assessments.


Subject(s)
Animal Feed , Food Contamination , Food , Legislation, Food , European Union , Food Additives , Food Microbiology , Food, Genetically Modified , Pesticide Residues , Plants, Genetically Modified , Risk Assessment
7.
J AOAC Int ; 88(1): 292-8, 2005.
Article in English | MEDLINE | ID: mdl-15759754

ABSTRACT

After the publication of high levels of acrylamide (AA) in food, many research activities started all over the world in order to determine the occurrence and the concentration of this substance in various types of food. As no validated methods were available at that time, interlaboratory studies on the determination of AA in food were of the highest priority. Under the boundary conditions of applying well-established evaluation schemes, the results of 2 studies conducted by the Federal Institute for Risk Assessment (BfR) in Germany and by the European Commission's Directorate General Joint Research Center (JRC) exhibited an overall acceptable performance of the participants in these studies. Nevertheless, many laboratories showed problems in determining AA in food with a complex matrix such as cocoa. The results of analysis also showed a broader variation of AA for samples with low AA concentrations and indicated a bias of the results obtained by gas chromatography-mass spectrometry without derivatization. Improvements of the performance of some laboratories appeared to be necessary.


Subject(s)
Acrylamide/analysis , Chemistry Techniques, Analytical/methods , Food Analysis/methods , Food , Gas Chromatography-Mass Spectrometry/methods , Acrylamide/toxicity , Bread , Cacao , European Union , Germany , Research Design , Risk Assessment , Solanum tuberosum , Time Factors
8.
J AOAC Int ; 87(5): 1179-88, 2004.
Article in English | MEDLINE | ID: mdl-15493676

ABSTRACT

The aim of the present study was to provide the official wine control authorities with an internationally validated method for the determination of 3-methoxy-1,2-propanediol (3-MPD) and cyclic diglycerols (CycDs)-both of which are recognized as impurities of technical glycerol-in different types of wine. Because glycerol gives a sweet flavor to wine and contributes to its full-body taste, an economic incentive is to add glycerol to a wine to mask its poor quality. Furthermore, it is known that glycerol, depending on whether it is produced from triglycerides or petrochemicals, may contain considerable amounts of 3-MPD in the first case or CycDs in the second. However, because these compounds are not natural wine components, it is possible to detect glycerol added to wine illegally by determining the above-mentioned by-products. To this end, one of the published methods was adopted, modified, and tested in a collaborative study. The method is based on gas chromatographic/mass spectrometric analysis of diethyl ether extracts after salting out with potassium carbonate. The interlaboratory study for the determination of 3-MPD and CycDs in wine was performed in 11 laboratories in 4 countries. Wine samples were prepared and sent to participants as 5 blind duplicate test materials and 1 single test material. The concentrations covered ranges of 0.1-0.8 mg/L for 3-MPD and 0.5-1.5 mg/L for CycDs. The precision of the method was within the range predicted by the Horwitz equation. HORRAT values obtained for 3-MPD ranged from 0.8 to 1.7, and those obtained for CycDs ranged from 0.9 to 1.3. Average recoveries were 104 and 109%, respectively.


Subject(s)
Diglycerides/analysis , Glyceryl Ethers/analysis , Wine/analysis , Gas Chromatography-Mass Spectrometry
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