Dietary glycation compounds - implications for human health.

The term "glycation compounds" comprises a wide range of structurally diverse compounds that are formed endogenously and in food via the Maillard reaction, a chemical reaction between reducing sugars and amino acids. Glycation compounds produced endogenously are considered to contribute to a range of diseases. This has led to the hypothesis that glycation compounds present in food may also cause adverse effects and thus pose a nutritional risk to human health. In this work, the Senate Commission on Food Safety (SKLM) of the German Research Foundation (DFG) summarized data on formation, occurrence, exposure and toxicity of glycation compounds (Part A) and systematically assessed potential associations between dietary intake of defined glycation compounds and disease, including allergy, diabetes, cardiovascular and renal disease, gut/gastrotoxicity, brain/cognitive impairment and cancer (Part B). A systematic search in Pubmed (Medline), Scopus and Web of Science using a combination of keywords defining individual glycation compounds and relevant disease patterns linked to the subject area of food, nutrition and diet retrieved 253 original publications relevant to the research question. Of these, only 192 were found to comply with previously defined quality criteria and were thus considered suitable to assess potential health risks of dietary glycation compounds. For each adverse health effect considered in this assessment, however, only limited numbers of human, animal and in vitro studies were identified. While studies in humans were often limited due to small cohort size, short study duration, and confounders, experimental studies in animals that allow for controlled exposure to individual glycation compounds provided some evidence for impaired glucose tolerance, insulin resistance, cardiovascular effects and renal injury in response to oral exposure to dicarbonyl compounds, albeit at dose levels by far exceeding estimated human exposures. The overall database was generally inconsistent or inconclusive. Based on this systematic review, the SKLM concludes that there is at present no convincing evidence for a causal association between dietary intake of glycation compounds and adverse health effects.

Considering the implication of endogenous glycation compounds in aging and disease, dietary exposure via consumption of an "AGE (advanced glycation end product) rich diet" is increasingly suggested to pose a potential health risk. However, studies attempting to assess an association between dietary glycation compounds and adverse health effects frequently suffer from insufficient chemical analysis of glycation compounds, including inadequate structural characterization and limited quantitative data. The Senate Commission on Food Safety (SKLM) of the German Research Foundation (DFG) previously defined quality criteria for studies designed to assess the effects of dietary glycation compounds on human health. The aim of the present work is to summarize data on formation, occurrence, exposure and toxicity of glycation compounds (Part A) and to systematically evaluate if the currently available scientific database allows for a conclusive assessment of potential health effects of defined glycation compounds (Part B).The term "glycation compounds" comprises a wide range of structurally diverse compounds that derive from the Maillard reaction, a chemical reaction between reducing carbohydrates and amino compounds that occurs during food processing. In the first stage of the Maillard reaction, reducing sugars such as glucose and fructose react for instance with the ε-amino group of lysine, which is most abundant in food ("glycation" of lysine). Subsequently, these primary reaction products undergo Amadori rearrangement to yield products (ARP) such as fructosyllysine (FL) from glucose and also Heyns rearrangement products (HRPs) such as glucosyl- and mannosyllysine from fructose. While ARPs are rapidly formed during food processing, they are not stable and undergo degradation reactions, predominantly to 1,2-dicarbonyl compounds such as glyoxal (GO), methylglyoxal (MGO) and 3-deoxyglucosone (3-DG), which are highly reactive. The last stage of the Maillard reaction is characterized predominantly by the reaction of these dicarbonyl compounds with nucleophilic groups of proteins. The side-chains of lysine and arginine residues as well as the N-termini of proteins are important reaction sites. Carboxyalkylated amino acids such as N-ε-carboxymethyllysine (CML) and N-ε-carboxyethyllysine (CEL) result from reaction of the ε-amino group of lysine with the dicarbonyl compounds GO and MGO. Dicarbonyl compounds with C5 or C6 chains can form cyclic pyrrole derivatives at the ε-amino group of lysine. The most important example for this reaction is pyrraline, which is formed from reaction of 3-DG and lysine. The reaction of dicarbonyl compounds with the guanidino group of arginine mainly leads to hydroimidazolones, of which the MGO-derived hydroimidazolone 1 (MG-H1) is best described in food systems.ARPs are the most abundant glycation products found in food. Up to 55% of the lysine residues in food may be modified to ARPs at the side-chain. Food items particularly rich in ARPs include bread, rusk, biscuits, chocolate, and powdered infant formulas. Exposure estimates range between 0.6­1.6 mg/kg body weight (bw), although exposure may be as high as 14.3 mg/kg bw in individuals consuming foods with extreme ARP concentrations. Foods particularly rich in dicarbonyl compounds include heat-treated or long-term stored items rich in reducing sugars such as jams, alternative sweeteners, soft drinks, honey, candies, cookies, and vinegars, especially balsamico-type vinegars. The main contributors to the daily intake of MGO, GO, and 3-DG are coffee and bread. Dietary exposure to dicarbonyl compounds has been estimated to range between 0.02­0.29 mg/kg bw/d for MGO, 0.04­0.16 mg/kg bw/d for GO, 0.14­2.3 mg/kg bw/d for 3-DG, and 0.08­0.13 mg/kg bw/d for 3-deoxygalactosone (3-DGal). Dietary intake of 5-hydroxymethylfurfural (HMF), which can be formed from 3-DG, is estimated to range between 0.0001­0.9 mg/kg bw/d. Exposure estimates for individual glycated amino acids range from 0.03­0.35 mg/kg bw/d for CML, 0.02­0.04 mg/kg bw/d for CEL and 0.19­0.41 mg/kg bw/d for MG-H1. From a model diet consisting of 1 L milk, 500 g bakery products and 400 mL coffee, an intake of pyrraline corresponding to 0.36 mg/kg bw/d for a 70 kg person was estimated.Quantitative analysis of individual glycation compounds or their metabolites in tissues or body fluids as well as their reaction products with amino acids, proteins or DNA may serve to monitor exposure to glycation compounds. However, since glycation compounds are also formed endogenously, these biomarkers reflect the totality of the exposure, making it inherently difficult to define the body burden due to dietary intake against the background of endogenous formation.Information on the toxicokinetics and toxicity of glycation compounds is scarce and mostly limited to the reactive dicarbonyl compounds GO, MGO, 3-DG, HMF, and individual glycated amino acids such as CML and CEL. Acute toxicity of dicarbonyl compounds is low to moderate. There are some data to suggest that rapid detoxification of dicarbonyls in the gastrointestinal tract and liver may limit their oral bioavailability. Biotransformation of GO and MGO occurs predominantly via the glutathione (GSH)-dependent glyoxalase system, and to a lesser extent via glutathione-independent aldo-keto-reductases, which are also responsible for biotransformation of 3-DG. GO, MGO and 3-DG readily react with DNA bases in vitro, giving rise to DNA adducts. There is clear evidence for genotoxicity of GO, MGO and 3-DG. Repeated dose toxicity studies on GO consistently reported reduced body weight gain concomitant with reduced food and water consumption but did not identify compound related changes in clinical chemistry and hematology or histopathological lesions. There is also no evidence for systemic carcinogenicity of GO and MGO based on the available studies. However, initiation/promotion studies indicate that oral exposure to GO may exhibit genotoxic and tumor promoting activity locally in the gastrointestinal tract. From a 2-year chronic toxicity and carcinogenicity study in rats, a NOAEL for systemic toxicity of GO administered via drinking water of 25 mg/kg bw was reported based on reduced body weight and erosions/ulcer in the glandular stomach. Other non-neoplastic and neoplastic lesions were not observed. Acute toxicity of HMF is also low. From a 90-day repeated dose toxicity study in mice, a NOAEL of 94 mg/kg bw was derived based on cytoplasmic alterations of proximal tubule epithelial cells of the kidney. HMF was mostly negative in in vitro genotoxicity tests, although positive findings for mutagenicity were obtained under conditions that promote formation of the chemically reactive sulfuric acid ester 5-sulfoxymethylfurfural. There is some evidence of carcinogenic activity of HMF in female B6C3F1 mice based on increased incidences of hepatocellular adenoma, but not in male mice and rats of both sexes. Although data on oral bioavailability of glycated amino acids are mostly limited to CML, it appears that glycated amino acids may be absorbed from the gastrointestinal tract after oral exposure to their free and protein bound form. Glycated amino acids that are not absorbed in the intestine may be subject to metabolism by the gut microbiome. Glycated amino acids present in the systemic circulation are rapidly eliminated via the urine. Acute oral toxicity of CML is low. Studies in mice and rats reported changes in clinical chemistry parameters indicative of impaired renal and hepatic function. However, these changes were not dose-related and not supported by histopathological evaluation.Previous risk assessments of individual glycation compounds did not identify a health concern at estimated human exposures (GO, HMF) but also noted the lack of data to draw firm conclusions on health risks associated with exposure to MGO.To identify potential associations between dietary intake of defined glycation compounds and disease a systematic review was carried out according to the Preferred Reporting Items for Systematic reviews and Meta-Analyses (PRISMA) model, applying the quality criteria previously defined by the SKLM. Using a combination of keywords defining individual glycation compounds and relevant disease patterns linked to the subject area of food, nutrition and diet, a systematic search in Pubmed (Medline), Scopus and Web of Science was performed. Although the present systematic review identified numerous studies that investigated an association between an "AGE-rich diet" and adverse health effects, only a subset of studies was found to comply with the quality criteria defined by the SKLM and was thus considered suitable to assess potential health risks of dietary glycation compounds.For each adverse health effect considered in this assessment, only limited numbers of human studies were identified. Although studies in humans offer the advantage of investigating effects at relevant human exposures, these studies did not provide compelling evidence for adverse effects of dietary glycation compounds. Animal studies identified in this systematic review provide some evidence for induction of impaired glucose tolerance, insulin resistance, cardiovascular effects and renal injury in response to oral exposure to GO and MGO as representatives of dicarbonyl compounds. Only limited evidence points to a link between high intake of glycated amino acids and metabolic disorders. However, these effects were typically reported to occur at dose levels that exceed human dietary exposure, often by several orders of magnitude. Unfortunately, most studies employed only one dose level, precluding characterization of dose-response and derivation of a point of departure for riskassessment. While in vitro studies provide some evidence for a potential mechanistic link between individual glycation compounds and presumed adverse health effects, the clinical and toxicological relevance of the in vitro findings is often limited by the use of high concentrations of glycation compounds that by far exceed human dietary exposure and by insufficient evidence for corresponding adverse effects in vivo. A key question that has not been adequately considered in most studies investigating systemic effects of glycation compounds is the extent of oral bioavailability of dietary glycation compounds, including the form in which MRPs may be taken up (e.g. free vs. peptide bound glycated amino acids). Understanding how much dietary glycation compounds really add to the significant endogenous background is critical to appraise the relevance of dietary MRPs for human health.While it appears mechanistically plausible that glycation of dietary allergens may affect their allergenic potential, the currently available data do not support the hypothesis that dietary glycation compounds may increase the risk for diet-induced allergies. There are no human studies addressing the immunological effects of dietary AGEs. Accordingly, there are no data on whether dietary AGEs promote the development of allergies, nor whether existing allergies are enhanced or attenuated. In numerous in vitro studies, the IgG/E binding ability of antigens and therefore their allergenic potential has been predominantly reported to be reduced by glycation. However, some in vitro studies showed that glycated proteins bind to receptors of immunological cells, and thus may have promoting effects on immune response and inflammation.Although experimental data from animal studies provide some evidence that high doses of individual glycation compounds such as MGO and protein-bound CML may produce certain adverse health effects, including diabetogenic, cardiovascular, metabolic and renal effects, the doses required to achieve these effects by far exceed human dietary exposures. Of note, in the only long-term study identified, a high dose of MGO administered via drinking water to mice for 18 months had no adverse effects on the kidneys, cardiovascular system, or development of diabetes.Experimental data from animal studies provide evidence that high doses of defined glycation compounds such as MGO or protein-bound CML may affect glucose homeostasis. However, the doses required to produce these effects markedly exceed human dietary exposure. Results from human studies are inconclusive: Three short-term intervention studies suggested that diets rich in AGEs may impair glucose homeostasis, whereas one recent intervention study and two observational studies failed to show such an effect.For the cardiovascular system, there is some evidence from in vitro and in vivo studies that high concentrations of MRPs, well above the dietary exposure of humans, may enhance inflammation in the cardiovascular system, induce endothelial damage, increase blood pressure and increase the risk of thrombosis. Only a limited number of human intervention studies investigated potential effects of short-term exposure and longer-term effects of glycation compounds on the cardiovascular system, and yielded inconsistent results. The few observational studies available either found no association between dietary MRP intake and cardiovascular function or even reported beneficial effects. Therefore, currently no definitive conclusion on potential acute and chronic effects of dietary MRPs on inflammation and cardiovascular function can be drawn. However, there is currently also no convincing evidence that potential adverse effects on the cardiovascular system are triggered by dietary MRP intake.Furthermore, human studies did not provide evidence for an adverse effect of dietary MRPs on kidney function. In animal studies with high levels of oral intake, MGO was reported to cause structural and functional effects in the kidney. Several studies show that the concentration of modified proteins and amino acids, such as CML, increases significantly in kidney tissue after oral intake. One study showed a negative effect of a high-temperature-treated diet containing increased CML concentrations on kidney structure integrity and impaired glomerular filtration. The causative relationship of accumulation of dietary MRPs and a functional decline of the kidneys, however, needs further confirmation.With regard to gut health, there is some evidence for alterations in gut microflora composition and the production of individual short-chain fatty acids (SCFAs) upon dietary exposure to glycation compounds. However, this has not been linked to adverse health effects in humans and may rather reflect adaptation of the gut microbiota to changing nutrients. In particular, a human observational study and several animal studies did not find a correlation between the intake of glycation compounds and increased intestinal inflammation. In animal studies, positive effects of glycation compounds on gut tissue damage and dysbiosis during colitis were described.Considering clear evidence for DNA reactivity and genotoxicity of the dicarbonyl compounds GO, MGO and 3-DG, it is plausible to suspect that dicarbonyl compounds may induce mutations and cancer. Although there is some evidence for tumor promoting activity of GO locally in the gastrointestinal tract, the only guideline-compatible chronic rodent bioassays reported erosions and ulcer in the glandular stomach but no treatment-related neoplastic lesions. A recent multinational cohort study with focus on CEL, CML, and MG-H1 found no evidence to support the hypothesis that dietary AGEs are linked to cancer risk.Evidence for an association between human exposure to dietary glycation compounds and detrimental effects on the brain and on cognitive performance is far from being compelling. No human studies fully complying with the defined quality criteria were identified. A few experimental studies reported neuroinflammation and cognitive impairment following dietary MRP exposure, but these can be considered indicative at best and do not support firm conclusions for human health. In addition to utilizing exceedingly high dosages of individual agents like CML, harsh processing conditions causing a multitude of major process-related changes do not allow to convincingly reconcile effects observed with measured/supposed contents of free and protein-bound CML alone.Overall, although dietary glycation compounds have been claimed to contribute to a wide range of adverse health effects, the present critical evaluation of the literature allows the conclusion that the available data are insufficient, inadequate or inconclusive and do not compellingly support the hypothesis of human health risks being related to the presence of glycation compounds in food. The study limitations detailed above, together with the fact that a large number of studies did not comply with the defined quality criteria and therefore had to be excluded highlight the importance of performing adequately designed human or animal studies to inform scientifically reliable health risk assessment.To achieve this, high quality, dependable scientific cooperation within various disciplines is pivotal.

Controversy on health-based guidance values for bisphenol A-the need of criteria for studies that serve as a basis for risk assessment.

Since 2006, the responsible regulatory bodies have proposed five health-based guidance values (HBGV) for bisphenol A (BPA) that differ by a factor of 250,000. This range of HBGVs covers a considerable part of the range from highly toxic to relatively non-toxic substances. As such heterogeneity of regulatory opinions is a challenge not only for scientific risk assessment but also for all stakeholders, the Senate Commission on Food Safety (SKLM) of the German Research Foundation (DFG) analyzed the reasons for the current discrepancy and used this example to suggest improvements for the process of HBGV recommendations. A key aspect for deriving a HBGV is the selection of appropriate studies that allow the identification of a point of departure (PoD) for risk assessment. In the case of BPA, the HBGV derived in the 2023 EFSA assessment was based on a study that reported an increase of Th17 cells in mice with a benchmark dose lower bound (BMDL40) of 0.53 µg/kg bw/day. However, this study does not comply with several criteria that are important for scientific risk assessment: (1) the selected end-point, Th17 cell frequency in the spleen of mice, is insufficiently understood with respect to health outcomes. (2) It is unclear, by which mechanism BPA may cause an increase in Th17 cell frequency. (3) It is unknown, if an increase of Th17 cell frequency in rodents is comparably observed in humans. (4) Toxicokinetics were not addressed. (5) Neither the raw data nor the experimental protocols are available. A further particularly important criterion (6) is independent data confirmation which is not available in the present case. Previous studies using other readouts did not observe immune-related adverse effects such as inflammation, even at doses orders of magnitude higher than in the Th17 cell-based study. The SKLM not only provides here key criteria for the use of such studies, but also suggests that the use of such a "checklist" requires a careful and comprehensive scientific judgement of each item. It is concluded that the Th17 cell-based study data do not represent an adequate basis for risk assessment of BPA.

Commentary of the SKLM to the EFSA opinion on risk assessment of N-nitrosamines in food.

Dietary exposure to N-nitrosamines has recently been assessed by the European Food Safety Authority (EFSA) to result in margins of exposure that are conceived to indicate concern with respect to human health risk. However, evidence from more than half a century of international research shows that N-nitroso compounds (NOC) can also be formed endogenously. In this commentary of the Senate Commission on Food Safety (SKLM) of the German Research Foundation (DFG), the complex metabolic and physiological biokinetics network of nitrate, nitrite and reactive nitrogen species is discussed with emphasis on its influence on endogenous NOC formation. Pioneering approaches to monitor endogenous NOC have been based on steady-state levels of N-nitrosodimethylamine (NDMA) in human blood and on DNA adduct levels in blood cells. Further NOC have not been considered yet to a comparable extent, although their generation from endogenous or exogenous precursors is to be expected. The evidence available to date indicates that endogenous NDMA exposure could exceed dietary exposure by about 2-3 orders of magnitude. These findings require consolidation by refined toxicokinetics and DNA adduct monitoring data to achieve a credible and comprehensive human health risk assessment.

The BlueScreen HC assay to predict the genotoxic potential of fragrance materials.

BlueScreen HC is a mammalian cell-based assay for measuring the genotoxicity and cytotoxicity of chemical compounds and mixtures. The BlueScreen HC assay has been utilized at the Research Institute for Fragrance Materials in a safety assessment program as a screening tool to prioritize fragrance materials for higher-tier testing, as supporting evidence when using a read-across approach, and as evidence to adjust the threshold of toxicological concern. Predictive values for the BlueScreen HC assay were evaluated based on the ability of the assay to predict the outcome of in vitro and in vivo mutagenicity and chromosomal damage genotoxicity assays. A set of 371 fragrance materials was assessed in the BlueScreen HC assay along with existing or newly generated in vitro and in vivo genotoxicity data. Based on a weight-of-evidence approach, the majority of materials in the data set were deemed negative and concluded not to have the potential to be genotoxic, while only a small proportion of materials were determined to show genotoxic effects in these assays. Analysis of the data set showed a combination of high positive agreement but low negative agreement between BlueScreen HC results, in vitro regulatory genotoxicity assays, and higher-tier test results. The BlueScreen HC assay did not generate any false negatives, thereby providing robustness when utilizing it as a high-throughput screening tool to evaluate the large inventory of fragrance materials. From the perspective of protecting public health, it is desirable to have no or minimal false negatives, as a false-negative result may incorrectly indicate the lack of a genotoxicity hazard. However, the assay did have a high percentage of false-positive results, resulting in poor positive predictivity of the in vitro genotoxicity test battery outcome. Overall, the assay generated 100% negative predictivity and 3.9% positive predictivity. In addition to the data set of 371 fragrance materials, 30 natural complex substances were evaluated for BlueScreen HC, Ames, and in vitro micronucleus assay, and a good correlation in all three assays was observed. Overall, while a positive result may have to be further investigated, these findings suggest that the BlueScreen HC assay can be a valuable screening tool to detect the genotoxic potential of fragrance materials and mixtures.

Salivary nitrate/nitrite and acetaldehyde in humans: potential combination effects in the upper gastrointestinal tract and possible consequences for the in vivo formation of N-nitroso compounds-a hypothesis.

Subsequent to the dietary uptake of nitrate/nitrite in combination with acetaldehyde/ethanol, combination effects resulting from the sustained endogenous exposure to nitrite and acetaldehyde may be expected. This may imply locoregional effects in the upper gastrointestinal tract as well as systemic effects, such as a potential influence on endogenous formation of N-nitroso compounds (NOC). Salivary concentrations of the individual components nitrate and nitrite and acetaldehyde are known to rise after ingestion, absorption and systemic distribution, thereby reflecting their respective plasma kinetics and parallel secretion through the salivary glands as well as the microbial/enzymatic metabolism in the oral cavity. Salivary excretion may also occur with certain drug molecules and food constituents and their metabolites. Therefore, putative combination effects in the oral cavity and the upper digestive tract may occur, but this has remained largely unexplored up to now. In this Guest Editorial, published evidence on exposure levels and biokinetics of nitrate/nitrite/NOx, NOC and acetaldehyde in the organism is reviewed and knowledge gaps concerning combination effects are identified. Research is suggested to be initiated to study the related unresolved issues.

Contribution to the ongoing discussion on fluoride toxicity.

Since the addition of fluoride to drinking water in the 1940s, there have been frequent and sometimes heated discussions regarding its benefits and risks. In a recently published review, we addressed the question if current exposure levels in Europe represent a risk to human health. This review was discussed in an editorial asking why we did not calculate benchmark doses (BMD) of fluoride neurotoxicity for humans. Here, we address the question, why it is problematic to calculate BMDs based on the currently available data. Briefly, the conclusions of the available studies are not homogeneous, reporting negative as well as positive results; moreover, the positive studies lack control of confounding factors such as the influence of well-known neurotoxicants. We also discuss the limitations of several further epidemiological studies that did not meet the inclusion criteria of our review. Finally, it is important to not only focus on epidemiological studies. Rather, risk analysis should consider all available data, including epidemiological, animal, as well as in vitro studies. Despite remaining uncertainties, the totality of evidence does not support the notion that fluoride should be considered a human developmental neurotoxicant at current exposure levels in European countries.

The safety evaluation of food flavoring substances: the role of genotoxicity studies.

The Flavor and Extract Manufacturers Association (FEMA) Expert Panel relies on the weight of evidence from all available data in the safety evaluation of flavoring substances. This process includes data from genotoxicity studies designed to assess the potential of a chemical agent to react with DNA or otherwise cause changes to DNA, either in vitro or in vivo. The Panel has reviewed a large number of in vitro and in vivo genotoxicity studies during the course of its ongoing safety evaluations of flavorings. The adherence of genotoxicity studies to standardized protocols and guidelines, the biological relevance of the results from those studies, and the human relevance of these studies are all important considerations in assessing whether the results raise specific concerns for genotoxic potential. The Panel evaluates genotoxicity studies not only for evidence of genotoxicity hazard, but also for the probability of risk to the consumer in the context of exposure from their use as flavoring substances. The majority of flavoring substances have given no indication of genotoxic potential in studies evaluated by the FEMA Expert Panel. Examples illustrating the assessment of genotoxicity data for flavoring substances and the consideration of the factors noted above are provided. The weight of evidence approach adopted by the FEMA Expert Panel leads to a rational assessment of risk associated with consumer intake of flavoring substances under the conditions of use.

Correction to: Revisiting the evidence for genotoxicity of acrylamide (AA), key to risk assessment of dietary AA exposure.

Unfortunately, the following errors occurred during the production process, compromising text understandability.

Revisiting the evidence for genotoxicity of acrylamide (AA), key to risk assessment of dietary AA exposure.

The weight of evidence pro/contra classifying the process-related food contaminant (PRC) acrylamide (AA) as a genotoxic carcinogen is reviewed. Current dietary AA exposure estimates reflect margins of exposure (MOEs) < 500. Several arguments support the view that AA may not act as a genotoxic carcinogen, especially not at consumer-relevant exposure levels: Biotransformation of AA into genotoxic glycidamide (GA) in primary rat hepatocytes is markedly slower than detoxifying coupling to glutathione (GS). Repeated feeding of rats with AA containing foods, bringing about uptake of 100 µg/kg/day of AA, resulted in dose x time-related buildup of AA-hemoglobin (Hb) adducts, whereas GA-Hb adducts remained within the background. Since hepatic oxidative biotransformation of AA into GA was proven by simultaneous urinary mercapturic acid monitoring it can be concluded that at this nutritional intake level any GA formed in the liver from AA is quantitatively coupled to GS to be excreted as mercapturic acid in urine. In an oral single dose-response study in rats, AA induced DNA N7-GA-Gua adducts dose-dependently in the high dose range (> 100 µg/kg b w). At variance, in the dose range below 100 µg/kg b.w. down to levels of average consumers exposure, DNA N7 -Gua lesions were found only sporadically, without dose dependence, and at levels close to the lower bound of similar human background DNA N7-Gua lesions. No DNA damage was detected by the comet assay within this low dose range. GA is a very weak mutagen, known to predominantly induce DNA N7-GA-Gua adducts, especially in the lower dose range. There is consensus that DNA N7-GA-Gua adducts exhibit rather low mutagenic potency. The low mutagenic potential of GA has further been evidenced by comparison to preactivated forms of other process-related contaminants, such as N-Nitroso compounds or polycyclic aromatic hydrocarbons, potent food borne mutagens/carcinogens. Toxicogenomic studies provide no evidence supporting a genotoxic mode of action (MOA), rather indicate effects on calcium signalling and cytoskeletal functions in rodent target organs. Rodent carcinogenicity studies show induction of strain- and species-specific neoplasms, with MOAs not considered likely predictive for human cancer risk. In summary, the overall evidence clearly argues for a nongenotoxic/nonmutagenic MOA underlying the neoplastic effects of AA in rodents. In consequence, a tolerable intake level (TDI) may be defined, guided by mechanistic elucidation of key adverse effects and supported by biomarker-based dosimetry in experimental systems and humans.

Mode of action-based risk assessment of genotoxic carcinogens.

The risk assessment of chemical carcinogens is one major task in toxicology. Even though exposure has been mitigated effectively during the last decades, low levels of carcinogenic substances in food and at the workplace are still present and often not completely avoidable. The distinction between genotoxic and non-genotoxic carcinogens has traditionally been regarded as particularly relevant for risk assessment, with the assumption of the existence of no-effect concentrations (threshold levels) in case of the latter group. In contrast, genotoxic carcinogens, their metabolic precursors and DNA reactive metabolites are considered to represent risk factors at all concentrations since even one or a few DNA lesions may in principle result in mutations and, thus, increase tumour risk. Within the current document, an updated risk evaluation for genotoxic carcinogens is proposed, based on mechanistic knowledge regarding the substance (group) under investigation, and taking into account recent improvements in analytical techniques used to quantify DNA lesions and mutations as well as "omics" approaches. Furthermore, wherever possible and appropriate, special attention is given to the integration of background levels of the same or comparable DNA lesions. Within part A, fundamental considerations highlight the terms hazard and risk with respect to DNA reactivity of genotoxic agents, as compared to non-genotoxic agents. Also, current methodologies used in genetic toxicology as well as in dosimetry of exposure are described. Special focus is given on the elucidation of modes of action (MOA) and on the relation between DNA damage and cancer risk. Part B addresses specific examples of genotoxic carcinogens, including those humans are exposed to exogenously and endogenously, such as formaldehyde, acetaldehyde and the corresponding alcohols as well as some alkylating agents, ethylene oxide, and acrylamide, but also examples resulting from exogenous sources like aflatoxin B1, allylalkoxybenzenes, 2-amino-3,8-dimethylimidazo[4,5-f] quinoxaline (MeIQx), benzo[a]pyrene and pyrrolizidine alkaloids. Additionally, special attention is given to some carcinogenic metal compounds, which are considered indirect genotoxins, by accelerating mutagenicity via interactions with the cellular response to DNA damage even at low exposure conditions. Part C finally encompasses conclusions and perspectives, suggesting a refined strategy for the assessment of the carcinogenic risk associated with an exposure to genotoxic compounds and addressing research needs.

Correction to: Mode of action-based risk assessment of genotoxic carcinogens.

The author would like to thank N. Bakhiya, S. Hessel-Pras, B. Sachse, and B. Dusemund for their support in the chapter about pyrrolizidine alkaloids.

Toxicity of fluoride: critical evaluation of evidence for human developmental neurotoxicity in epidemiological studies, animal experiments and in vitro analyses.

Recently, epidemiological studies have suggested that fluoride is a human developmental neurotoxicant that reduces measures of intelligence in children, placing it into the same category as toxic metals (lead, methylmercury, arsenic) and polychlorinated biphenyls. If true, this assessment would be highly relevant considering the widespread fluoridation of drinking water and the worldwide use of fluoride in oral hygiene products such as toothpaste. To gain a deeper understanding of these assertions, we reviewed the levels of human exposure, as well as results from animal experiments, particularly focusing on developmental toxicity, and the molecular mechanisms by which fluoride can cause adverse effects. Moreover, in vitro studies investigating fluoride in neuronal cells and precursor/stem cells were analyzed, and 23 epidemiological studies published since 2012 were considered. The results show that the margin of exposure (MoE) between no observed adverse effect levels (NOAELs) in animal studies and the current adequate intake (AI) of fluoride (50 µg/kg b.w./day) in humans ranges between 50 and 210, depending on the specific animal experiment used as reference. Even for unusually high fluoride exposure levels, an MoE of at least ten was obtained. Furthermore, concentrations of fluoride in human plasma are much lower than fluoride concentrations, causing effects in cell cultures. In contrast, 21 of 23 recent epidemiological studies report an association between high fluoride exposure and reduced intelligence. The discrepancy between experimental and epidemiological evidence may be reconciled with deficiencies inherent in most of these epidemiological studies on a putative association between fluoride and intelligence, especially with respect to adequate consideration of potential confounding factors, e.g., socioeconomic status, residence, breast feeding, low birth weight, maternal intelligence, and exposure to other neurotoxic chemicals. In conclusion, based on the totality of currently available scientific evidence, the present review does not support the presumption that fluoride should be assessed as a human developmental neurotoxicant at the current exposure levels in Europe.

Biomonitoring of nutritional acrylamide intake by consumers without dietary preferences as compared to vegans.

Acrylamide (AA) is a heat-induced food contaminant considered as genotoxic carcinogen. The present study investigated the influence of nutritional and lifestyle preferences on human AA exposure. A 10-day human study was performed with ten volunteers without nutritional preferences (omnivores) and ten vegans. Volunteers self-reported their daily routine and dietary habits. Overall mean AA intake, calculated from contents of diet duplicates, was 0.32 ± 0.19 µg/kg body weight (bw)/day with marked inter-day and inter-volunteer variabilities. Vegans ingested more AA (0.38 ± 0.23 µg/kg bw/day) than omnivore volunteers without dietary restrictions (0.26 ± 0.10 µg/kg bw/day). Excretion kinetics of urinary AA-related mercapturic acids N-acetyl-S-(2-carbamoylethyl)-L-cysteine and N-acetyl-S-(2-hydroxy-2-carbamoylethyl)-L-cysteine were essentially concordant with the respective dietary AA intake. Disproportionately enhanced AA-related biomarker excretion could be traced back to reportedly inadvertent, passive exposure to tobacco and/or fire smoke, as evidenced by the respective urinary exposure biomarkers, cotinine and N-acetyl-S-(2-cyanoethyl)-L-cysteine. Although the study is based on the comparison of small volunteer groups, the results confirm the association of AA exposure biomarkers with documented dietary preferences and lifestyle factors. Some additional contribution of endogenous background AA exposure was demonstrated individually. Disproportionately enhanced AA exposure is suggested to result from passive exposure to tobacco and/or barbecue smoke.

Exposure assessment of process-related contaminants in food by biomarker monitoring.

Exposure assessment is a fundamental part of the risk assessment paradigm, but can often present a number of challenges and uncertainties. This is especially the case for process contaminants formed during the processing, e.g. heating of food, since they are in part highly reactive and/or volatile, thus making exposure assessment by analysing contents in food unreliable. New approaches are therefore required to accurately assess consumer exposure and thus better inform the risk assessment. Such novel approaches may include the use of biomarkers, physiologically based kinetic (PBK) modelling-facilitated reverse dosimetry, and/or duplicate diet studies. This review focuses on the state of the art with respect to the use of biomarkers of exposure for the process contaminants acrylamide, 3-MCPD esters, glycidyl esters, furan and acrolein. From the overview presented, it becomes clear that the field of assessing human exposure to process-related contaminants in food by biomarker monitoring is promising and strongly developing. The current state of the art as well as the existing data gaps and challenges for the future were defined. They include (1) using PBK modelling and duplicate diet studies to establish, preferably in humans, correlations between external exposure and biomarkers; (2) elucidation of the possible endogenous formation of the process-related contaminants and the resulting biomarker levels; (3) the influence of inter-individual variations and how to include that in the biomarker-based exposure predictions; (4) the correction for confounding factors; (5) the value of the different biomarkers in relation to exposure scenario's and risk assessment, and (6) the possibilities of novel methodologies. In spite of these challenges it can be concluded that biomarker-based exposure assessment provides a unique opportunity to more accurately assess consumer exposure to process-related contaminants in food and thus to better inform risk assessment.

Biomarker monitoring of controlled dietary acrylamide exposure indicates consistent human endogenous background.

The aim of the present study was to explore the relation of controlled dietary acrylamide (AA) intake with the excretion of AA-related urinary mercapturic acids (MA), N-acetyl-S-(carbamoylethyl)-L-cysteine (AAMA) and N-acetyl-S-(1-carbamoyl-2-hydroxyethyl)-L-cysteine (GAMA). Excretion kinetics of these short-term exposure biomarkers were monitored under strictly controlled conditions within a duplicate diet human intervention study. One study arm (group A, n = 6) ingested AA via coffee (0.15-0.17 µg/kg bw) on day 6 and in a meal containing an upper exposure level of AA (14.1-15.9 µg/kg bw) on day 10. The other arm (group B) was on AA minimized diet (washout, 0.05-0.06 µg/kg bw) throughout the whole 13-day study period. On day 6, these volunteers ingested 13C3D3-AA (1 µg/kg bw). In both arms, urinary MA excretion was continuously monitored and blood samples were taken to determine hemoglobin adducts. Ingestion of four cups of coffee resulted in a slightly enhanced short-term biomarker response within the background range of group B. At the end of the 13-day washout period, group B excreted an AAMA baseline level of 0.14 ± 0.10 µmol/d although AA intake was only about 0.06 µmol/d. This sustained over-proportional AAMA background suggested an endogenous AA baseline exposure level of 0.3-0.4 µg/kg bw/d. The excretion of 13C3D3-AA was practically complete within 72-96 h which rules out delayed release of AA (or any other MA precursor) from deep body compartments. The results provide compelling support for the hypothesis of a sustained endogenous AA formation in the human body.

Assessing the potential impact on the thyroid axis of environmentally relevant food constituents/contaminants in humans.

Occurrence and mode of action of potentially relevant goitrogens in human nutrition and their mode of action (MOA) are reviewed, with special focus on the anionic iodine uptake inhibitors perchlorate (PER), thiocyanate (SCN) and nitrate (NO3). Epidemiological studies suggest persistent halogenated organic contaminants and phthalates as well as certain antimicrobials to deserve increased attention. This also applies to natural goitrogens, including polyphenols and glucosinolates, food constituents with limited data density concerning human exposure. Glucosinolates present in animal feed are presumed to contribute to SCN transfer into milk and milk products. PER, SCN and NO3 are well-investigated environmental goitrogens in terms of MOA and relative potency. There is compelling evidence from biomarker monitoring that the exposure to the goitrogens SCN and NO3 via human nutrition exceeds that of PER by orders of magnitude. The day-to-day variation in dietary intake of these substances (and of iodide) is concluded to entail corresponding variations in thyroidal iodide uptake, not considered as adverse to health or toxicologically relevant. Such normal variability of nutritional goitrogen uptake provides an obvious explanation for the variability in radioactive iodine uptake (RAIU) measurements observed in healthy individuals. Based on available data, a 20 % change in the thyroidal uptake of iodide is derived as threshold value for a biologically meaningful change induced by perchlorate and other goitrogens with the same MOA. We propose this value to be used as the critical effect size or benchmark response in benchmark dose analysis of human RAIU data. The resulting BMDL20 is 0.0165 mg/kg bw/day or 16.5 µg/kg bw/day. Applying a factor of 4, to allow for inter-human differences in toxicokinetics, leads to a TDI for perchlorate of 4 µg/kg bw/day.

Monitoring urinary mercapturic acids as biomarkers of human dietary exposure to acrylamide in combination with acrylamide uptake assessment based on duplicate diets.

The present human intervention study investigated the relation between the intake of acrylamide (AA) in diets with minimized, low, and high AA contents and the levels of urinary exposure biomarkers. As biomarkers, the mercapturic acids, N-acetyl-S-(carbamoylethyl)-L-cysteine (AAMA), and N-acetyl-S-(1-carbamoyl-2-hydroxyethyl)-L-cysteine (GAMA) were monitored. The study was performed with 14 healthy male volunteers over a period of 9 days, under controlled conditions excluding any inadvertent AA exposure. Dietary exposure to AA was measured by determining AA contents in duplicates of all meals consumed by the volunteers. The study design included an initial washout period of 3 days on AA-minimized diet, resulting in dietary AA exposure not exceeding 41 ng/kg bw/d. Identical washout periods of 2 days each followed the AA exposure days (day 4, low exposure, and day 7, high exposure). At the respective AA intake days, volunteers ingested 0.6-0.8 (low exposure) or 1.3-1.8 (high exposure) µg AA/kg bw/d with their food. Both low and high AA intakes resulted in an AAMA output within 72 h corresponding to 58 % of the respective AA intake. At the end of the initial 3-day washout period, an AAMA baseline level of 93 ± 31 nmol/d was recorded, suggestive for an assumed net AA baseline exposure level of 0.2-0.3 µg AA/kg bw/d.