| Literature DB >> 22069602 |
Olivier Puel1, Pierre Galtier, Isabelle P Oswald.
Abstract
Patulin is a toxic chemical contaminant produced by several species of mold, especially within Aspergillus, Penicillium and Byssochlamys. It is the most common mycotoxin found in apples and apple-derived products such as juice, cider, compotes and other food intended for young children. Exposure to this mycotoxin is associated with immunological, neurological and gastrointestinal outcomes. Assessment of the health risks due to patulin consumption by humans has led many countries to regulate the quantity in food. A full understanding of the molecular genetics of patulin biosynthesis is incomplete, unlike other regulated mycotoxins (aflatoxins, trichothecenes and fumonisins), although the chemical structures of patulin precursors are now known. The biosynthetic pathway consists of approximately 10 steps, as suggested by biochemical studies. Recently, a cluster of 15 genes involved in patulin biosynthesis was reported, containing characterized enzymes, a regulation factor and transporter genes. This review includes information on the current understanding of the mechanisms of patulin toxinogenesis and summarizes its toxicological effects.Entities:
Keywords: biosynthesis; patulin; polyketide; toxicity
Mesh:
Substances:
Year: 2010 PMID: 22069602 PMCID: PMC3153204 DOI: 10.3390/toxins2040613
Source DB: PubMed Journal: Toxins (Basel) ISSN: 2072-6651 Impact factor: 4.546
Figure 1An apple contaminated by Penicillium expansum.
Figure 2Scheme of patulin biosynthetic pathways. Adapted from [29,41,107].
Figure 3Patulin gene cluster in A. clavatus and comparison of secondary metabolite gene clusters in three other fungi species that contain some genes related to patulin production. Grey indicates genes of the patulin cluster; white indicates genes adjacent to the patulin cluster. The black arrows in T. stipitatus represent genes that are not present in the patulin gene cluster.
Summary of sub-chronic studies describing the effects of patulin.
| Species | Dose | Duration | Observations | Reference |
|---|---|---|---|---|
| Mice | 24–36 mg/kg b.w. every day or every other day | 14 days | Intestinal disorders | [ |
| Rat | 28–41 mg/kg b.w. every day or every other day | 14 days | Intestinal disorders | [ |
| Rat | 25–295 mg/L in drinking water | 28 days | Decreased weight | [ |
| Decreased Cl creatinine | ||||
| Gastric ulcers with high doses | ||||
| Rat | 0.1 mg/kg b.w. every day | 30 days | Decreased lipids | [ |
| Decreased triglycerides | ||||
| Increased cholesterol | ||||
| Inhibition of intestinal ATPase | ||||
| Rat | 6–150 mg/L in drinking water | 13 weeks | Decreased food intake | [ |
| Decreased weight with high doses | ||||
| Rat | 0.1 mg/kg b.w. every day | 60 & 90 days | Increased testosterone and LH levels | [ |
| Alteration of testis and thyroid morphology | ||||
| Rat | 0.1 mg/kg b.w. every day | 60 & 90 days | Decreased sperm count | [ |
| Alteration in sperm morphology | ||||
| Hamster | 16 mg/kg b.w. every day or every other day | 14 days | Intestinal disorders | [ |
| Chicken | 100 µg every other day | 30 days | Intestinal disorders | [ |
| Alteration of renal function | ||||
| Inhibition of intestinal and renal ATPases | ||||
| Monkey | 5; 50; 500 µg/kg b.w. then 5 mg/kg b.w. every day | 30 days 45 days | No toxicity | [ |
| Food refusal (high dose) | ||||
| Alteration of renal function (medium dose) |