Laurence Ribonnet

Molecular and cellular effects of food contaminants and secondary plant components and their plausible interactions at the intestinal level

The intestinal mucosa is not simply a barrier allowing entry of compounds such as nutrients or chemicals, and restricting that of others. Intestinal cells and activities perform selective absorption, biotransformations and efflux back to the lumen. Furthermore, food substances affect both bioavailability and intestinal function. Some are able to act as transcriptional regulators and enzyme modulators. This review points out plausible interactions between food contaminants and/or natural constituents at molecular and cellular levels and focuses on the effects of classical (pesticides and veterinary drugs), environmental (heavy metals, PCBs, dioxins, etc.) and food processing generated (PAHs, heterocyclic amines, etc.) contaminants on absorption, metabolism and efflux. Special attention is given to secondary metabolites of molds (mycotoxins) and plants (polyphenols). Molecular targets are briefly described as well as regulation mechanisms. Where possible, data referred to deal with human intestinal functions in vivo, and with in vitro studies on human intestinal Caco-2 cells; however, since data related to the intestine are rather scarce, effects on molecular targets in liver are also considered. This review also points out the urgent need for fully validated high throughput in vitro tools to screen combinations of substances, at realistic intestinal concentrations. A higher priority could then be given to combinations of nutrients, xenobiotics and food contaminants, with hazardous or beneficial impacts on human health.

CYP1A1 induction and CYP3A4 inhibition by the fungicide imazalil in the human intestinal Caco-2 cells - comparison with other conazole pesticides.

Imazalil (IMA) is a widely used imidazole-antifungal pesticide and, therefore, a food contaminant. This compound is also used as a drug (enilconazole). As intestine is the first site of exposure to ingested drugs and pollutants, we have investigated the effects of IMA, at realistic intestinal concentrations, on xenobiotic-metabolizing enzymes and efflux pumps by using Caco-2 cells, as a validated in vitro model of the human intestinal absorptive epithelium. For comparison, other conazole fungicides, i.e. ketoconazole, propiconazole and tebuconazole, were also studied. IMA induced cytochrome P450 (CYP) 1A1 activity to the same extent as benzo(a)pyrene (B(a)P) or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), in a dose- and time-dependent manner. Cell-free aryl hydrocarbon receptor (AhR) binding assay and reporter gene assay suggested that IMA is not an AhR-ligand, implying that IMA-mediated induction should involve an AhR-independent pathway. Moreover, IMA strongly inhibited the CYP3A4 activity in 1,25-vitamin D(3)-induced Caco-2 cells. The other fungicides had weak or nil effects on CYP activities. Study of the apical efflux pump activities revealed that ketoconazole inhibited both P-glycoprotein (Pgp) and multidrug resistance-associated protein 2 (MRP-2) or breast cancer resistance protein (BCRP), whereas IMA and other fungicides did not. Our results imply that coingestion of IMA-contaminated food and CYP3A4- or CYP1A1-metabolizable drugs or chemicals could lead to drug bioavailability modulation or toxicological interactions, with possible adverse effects for human health.

Modulation of CYP1A1 activity by a Ginkgo biloba extract in the human intestinal Caco-2 cells

Ginkgo biloba is a widely consumed dietary supplement. Some dietary active compounds modulate the activity of biotransformation enzymes inside the enterocytes and more interestingly of cytochrome P-450 1A1 (CYP1A1). This enzyme is of a particular interest because of its implication in the metabolism of some exogenous pro-carcinogens or endogenous molecules. In the present work, we have used Caco-2 cells to study the effect of a standard reference material of a Ginkgo biloba extract (GBE) (10-400 μg/ml), as well as of its major individual active compounds (kaempferol, quercetin, isorhamnetin, ginkgolides and bilobalide), alone or in mixtures, at realistic intestinal concentrations, on the induction of CYP1A1 activity, in the presence or absence of benzo[a]pyrene (B[a]P) (0.1 μg/ml), a well-known CYP1A1 inducer. 3-O-rutinosides of kaempferol, quercetin and isorhamnetin were also tested. We have demonstrated a strong induction (p < 0.005) of CYP1A1 activity and a slight, but significant (p < 0.005), decrease of this activity in the presence of B[a]P by the GBE at the realistic exposure level of 100 μg/ml. The inductive effect was explained, in part, by quercetin and kaempferol after 24h exposure while unknown compounds seem to be responsible for the strong CYP1A1 induction observed after 6h exposure. The inhibitory potency of flavonols on CYP1A1 activity in presence of B[a]P was much stronger for the aglycones than for the 3-O-rutinosides, explaining the slight effect observed with the GBE, mainly composed of glycosylated flavonoids. These results indicate that GBEs may disturb intestinal CYP1A1 activity and, in turn, affect the metabolism of other compounds. The present paper thus highlights the necessity to take these side effects into account when administrating Ginkgo biloba herbal supplements.

Potential of an in vitro toolbox combined with exposure data as a first step for the risk assessment of dietary chemical contaminants.

In vitro risk assessment of dietary contaminants has become a priority in human food safety. This paper proposes an in vitro approach associating different complementary tools in an original toolbox and aims to improve the assessment of the toxicological impact of dietary contaminants at realistic human exposure levels, with a special focus on the intestinal compartment. The system is based on the use of four complementary cellular tools, namely stress gene induction in transgenic strains of Escherichia coli, modulation of the activity of key biotransformation enzymes (cytochrome P-450 (CYP) 1A1 and 3A4) in a human intestinal cell line, and activation of aryl hydrocarbon receptor (AhR) and oestrogenic receptor (ER)-dependent genes in agonistic and antagonistic assays with luciferase reporter cells. It was applied to four chosen model molecules: ochratoxin A (OTA) and deoxynivalenol (DON), two common food-borne mycotoxins, and imazalil (IMA) and benomyl (BEN), two fungicides widely occurring in foodstuffs. All these assays were performed at or around a realistic intestinal concentration, determined through a deterministic approach based on the calculation of a theoretical maximum daily intake (TMDI). Using the four model molecules, it is clearly highlighted that induction of CYP1A1 activity and inhibition of CYP3A4 activity occurred in Caco-2 cells at a realistic intestinal concentration of IMA. Furthermore, some bacterial stress genes were induced in a range of realistic concentrations, following exposure to DON and IMA. In addition, BEN clearly provoked an ER agonistic activity in a human oestrogen sensitive reporter cell line. All these results are in accordance with the literature, suggesting that the in vitro toolbox constitutes an interesting approach in order to obtain a first ‘fingerprint’ of dietary contaminants at realistic human exposure for further risk assessment.