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The toxicological assessment of chemically complex food matrices (CCFM) usually is very time consuming, expensive and uses many animal studies. Improvements to obtain a more efficient assessment process remain limited as long as we retain traditional approaches to toxicological risk assessment. New concepts would be needed to achieve real innovations in risk assessment. The threshold of toxicological concern (TTC) potentially is such a concept that has existed for many years and recently has been further developed.The safety of CCFM is difficult to assess as there are numerous unknown substances present (often referred to as 'Forest-of-Peaks' in chromatographic analysis). Usually, for the evaluation of CCFM, a full safety assessment approach involving animal studies is needed, but the exposure to most substances is low and TTC might be applicable. However, to apply TTC efficiently to CCFM, a strategy is needed to deal with large numbers of unknowns (substances of which structural information is lacking). Therefore, we have drafted a framework for application of TTC in safety assessment of CCFM. This paper describes the criteria and development of the framework proposing a stepwise approach for the application of TTC in safety assessment of CCFM and future developments required. © 2010 Elsevier Ltd.

Objectives: The critical health effects of formaldehyde exposure include sensory irritation and the potential to induce tumours in the upper respiratory tract. In literature, a concentration as low as 0.24 ppm has been reported to be irritating to the respiratory tract in humans. Nasal tumour-inducing levels in experimental animals seem to be 1-2 orders of magnitude larger. In this paper, the subjectively measured sensory irritation threshold levels in humans are discussed in line with findings obtained in animal experiments. In addition, a Benchmark dose (BMD) analysis of sensory irritation was used to estimate response incidences at different formaldehyde concentrations. Methods: Data on respiratory irritation and carcinogenicity of formaldehyde were retrieved from public literature and discussed. BMD analysis was carried out on human volunteer studies using the US-EPA BMD software. Results: Subjective measures of irritation were the major data found in humans to examine sensory (eye and nasal) irritation; only one study reported objectively measured eye irritation. On a normalized scale, mild/slight eye irritation was observed at levels ≥1 ppm, and mild/slight respiratory tract irritation at levels ≥2 ppm. With the BMD software, it was estimated that at a level of 1 ppm, only 9.5% of healthy volunteers experience 'moderate' (i.e., annoying) eye irritation (95% upper confidence limit). An important factor modulating the reported levels of irritation and health symptoms most probably includes the perception of odour intensity. In several studies, the 0-ppm control condition was missing. From the results of the long-term inhalation toxicity studies in experimental animals, a level of 1 ppm formaldehyde has been considered a NOAEL for nasal injury. Conclusions: Sensory irritation is first observed at levels of 1 ppm and higher. From both human and animal studies, it was concluded that at airborne levels for which the prevalence of sensory irritation is minimal both in incidence and degree (i.e.

Health risks resulting from occupational exposure to chemicals are controlled by the establishment of acceptable dermal and respiratory exposure levels. Due to a lack of route-specific toxicity data, acceptable levels are frequently established by means of route-to-route extrapolation. A pitfall in route-to-route extrapolation is the occurrence of local effects. Often, the results of acute irritation studies are used to assess the likelihood of the occurrence of local effects also following repeated exposure and thereby the validity of route-to-route extrapolation. We questioned this working practice and considered whether local effects observed in a given study are of any predictive value with respect to the occurrence of local effects after repeated exposure. Our database analysis indicates that substances inducing skin and/or eye irritation frequently induce local effects after repeated respiratory exposure. In contrast, observations made in any type of study show little or no positive predictive value for the occurrence of local effects after repeated dermal exposure. Notably, the absence of any indication of local effects in any type of study does not exclude the occurrence of local effects on repeated dermal or respiratory exposure. We conclude that the presumed reliability of route-to-route extrapolation in the absence of route-specific toxicity data can be questioned. © 2002 Elsevier Science (USA). Chemicals/CAS: Irritants