Glyphosate is the most widely used herbicide worldwide. It is a broad spectrum herbicide and its agricultural uses increased considerably after the development of glyphosate-resistant genetically modified (GM) varieties. Since glyphosate was introduced in 1974, all regulatory assessments have established that glyphosate has low hazard potential to mammals, however, the International Agency for Research on Cancer (IARC) concluded in March 2015 that it is probably carcinogenic. The IARC conclusion was not confirmed by the EU assessment or the recent joint WHO/FAO evaluation, both using additional evidence. Glyphosate is not the first topic of disagreement between IARC and regulatory evaluations, but has received greater attention. This review presents the scientific basis of the glyphosate health assessment conducted within the European Union (EU) renewal process, and explains the differences in the carcinogenicity assessment with IARC. Use of different data sets, particularly on long-term toxicity/carcinogenicity in rodents, could partially explain the divergent views; but methodological differences in the evaluation of the available evidence have been identified. The EU assessment did not identify a carcinogenicity hazard, revised the toxicological profile proposing new toxicological reference values, and conducted a risk assessment for some representatives uses. Two complementary exposure assessments, human-biomonitoring and food-residues-monitoring, suggests that actual exposure levels are below these reference values and do not represent a public concern.Electronic supplementary materialThe online version of this article (doi:10.1007/s00204-017-1962-5) contains supplementary material, which is available to authorized users.
For active substances in plant protection products (PPP) with well defined urinary elimination, no potential for accumulation and virtually no metabolism, measuring of urine levels could be a powerful tool for human biomonitoring. Such data may provide reliable estimates of actual internal human exposure that can be compared to appropriate reference values, such as the 'acceptable daily intake (ADI)' or the 'acceptable operator exposure level (AOEL)'. Traces of the active compound glyphosate were found in human urine samples, probably resulting either from occupational use for plant protection purposes or from dietary intake of residues. A critical review and comparison of data obtained in a total of seven studies from Europe and the US was performed. The conclusion can be drawn that no health concern was revealed because the resulting exposure estimates were by magnitudes lower than the ADI or the AOEL. The expected internal exposure was clearly below the worst-case predictions made in the evaluation of glyphosate as performed for the renewal of its approval within the European Union. However, differences in the extent of exposure with regard to the predominant occupational and dietary exposure routes and between Europe and North America became apparent.
The toxicological relevance of effects observed at molecular stage, which occur at dose levels well below classical no-observed adverse effect levels is currently subject to controversial scientific debate. While the importance of molecular effects for the identification of a mode of action or an adverse outcome pathway is undisputed, their impact for other regulatory purposes remains uncertain. Here, we report the results of a 28-day rat-feeding study including three widely used hepatotoxic (tri)azole fungicides (cyproconazole, epoxiconazole and prochloraz) administered individually at five dose levels, ranging from slightly above the reference values to a clear toxic effect dose. Parameters analysed included pathology, histopathology, clinical chemistry and particularly effects on the molecular level. Since azole fungicides are considered to cause liver toxicity by a mechanism involving the constitutive androstane receptor (CAR), a known CAR activator (phenobarbital, PB) was administered to investigate potential similarities between triazoles and PB-mediated liver toxicity by pathway-focused gene expression analysis. Our results show an increase in liver weights and additionally histopathological changes (hepatocellular hypertrophy) for all substances at the top dose levels. The effects on liver weight were most pronounced for cyproconazole by which also the animals receiving the next lower dose were affected. In addition, vacuolisation of hepatocytes was observed at the top dose level. No such findings were obtained with any substance at lower doses to which consumers and operators might be exposed to. In contrast, the expression of sensitive marker genes (like some cytochrome-P-450 isoforms) was significantly affected also at the lower dose levels. While some of these changes, like the induction of genes related to fatty acid and phospholipid metabolism (e.g. Fasn, Fat/Cd36, Ppargc1a) or xenobiotic metabolism (Cyp1a1, Cyp2b1, Cyp3a2), could be associated with high dose effects like hepatocellular vacuolisation or hypertrophy, a histopathological correlate was lacking for others.
Consumers are exposed to multiple residues of different pesticides via the diet. Therefore, EU legislation for pesticides requires the evaluation of single active substances as well as the consideration of combination effects. Hence the analysis of combined effects of substances in a broad dose range represents a key challenge to current experimental and regulatory toxicology. Here we report evidence for additive effects for (tri)azole fungicides, a widely used group of antifungal agents, in the human placental cell line Jeg-3. In addition to the triazoles cyproconazole, epoxiconazole, flusilazole and tebuconazole and the azole fungicide prochloraz also pesticides from other chemical classes assumed to act via different modes of action (i.e., the organophosphate chlorpyrifos and the triazinylsulfonylurea herbicide triflusulfuron-methyl) were investigated. Endpoints analysed include synthesis of steroid hormone production (progesterone and estradiol) and gene expression of steroidogenic and non-steroidogenic cytochrome-P-450 (CYP) enzymes. For the triazoles and prochloraz, a dose dependent inhibition of progesterone production was observed and additive effects could be confirmed for several combinations of these substances in vitro. The non-triazoles chlorpyrifos and triflusulfuron-methyl did not affect this endpoint and, in line with this finding, no additivity was observed when these substances were applied in mixtures with prochloraz. While prochloraz slightly increased aromatase expression and estradiol production and triflusulfuron-methyl decreased estradiol production, none of the other substances had effects on the expression levels of steroidogenic CYP-enzymes in Jeg-3 cells. For some triazoles, prochloraz and chlorpyrifos a significant induction of CYP1A1 mRNA expression and potential combination effects for this endpoint were observed. Inhibition of CYP1A1 mRNA induction by the AhR inhibitor CH223191 indicated AhR receptor dependence of this effect.
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