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Rapid immunochemical screening method for aflatoxin B1 in human and animal urine.

A method has been developed to determine the presence of aflatoxin B1 in the urine of animals (including humans) by utilizing commercial immunochemical kits that can be used in the field. Urine is treated with diatomaceous earth and filtered to clarify the sample; 2-3 ppb aflatoxin B1, corresponding to about 300 ppb in the ingested feed/food, can be detected in the filtered urine without further purification. To improve sensitivity, the urine filtrate is passed through a C18 solid phase column to extract the aflatoxin. The column is washed with acetonitrile-water (15 + 85) and water, aflatoxin B1 is eluted with methanol-water (7 + 3), and water is added to the eluate, which is then tested for aflatoxin with the test kit. The limit of detection is 0.2 ppb, reflecting consumption of 40 ppb or more aflatoxin in the feed/food. When the initial sample volume is adequate, purification through the C18 column step is usually sufficient. For limited sample volumes, the eluate from the C18 column is mixed with water, added to an immunosorbent affinity column, and washed with water to remove excess sample matrix and impurities. Aflatoxin B1 is eluted with acetonitrile. The extract is evaporated under nitrogen and the residue is redissolved in methanol-water (25 + 75). At this purification stage, the limit of detection is reduced to 0.05 ppb.

Aflatoxin B1↗

Indole-3-carbinol and beta-naphthoflavone induction of aflatoxin B1 metabolism and cytochromes P-450 associated with bioactivation and detoxication of aflatoxin B1 in the rat.

Aflatoxin B1 (AFB1) is a highly hepatotoxic and hepatocarcinogenic secondary metabolite of the grain mold Aspergillus flavus and related fungi. Indole-3-carbinol (I3C), found in cruciferous vegetables, can both inhibit and promote AFB1-induced carcinogenesis. We have examined the influence of dietary treatment with I3C and the well-known Ah receptor agonist beta-naphthoflavone (BNF) on the relative levels of different cytochrome P-450 (CYP) isoforms known to metabolize AFB1 in male Fischer 344 rats. After 7 days of feeding 0.2% I3C or 0.04% BNF, alone or in combination, the relative levels of hepatic CYP1A1, 1A2, 2B1/2, 2C11, and 3A were assessed by laser densitometry of Western blots. Both diets containing I3C markedly increased band densities of CYP1A1 (up to 24-fold), 1A2 (3.1-fold), and 3A1/2 (3.8-fold), and had lesser effects on the levels of 2B1/2 (1.8-fold) and no effect on CYP2C11. BNF also strongly increased band densities of CYP1A1 (12-fold) and 1A2 (2.7-fold), but had no effect on the levels of CYP2B1/2 or 3A1/2 band densities, and repressed those of CYP2C11 (2-fold). In addition, we examined the in vitro hepatic microsomal metabolism of AFB1 at 16, 124, and 512 microM substrate levels. Diets containing I3C elevated initial rates of AFM1 (a detoxication product) production 18.6- to 19.2-fold over control at 16 microM AFB1, which declined to 7.8- to 9.5-fold at 512 microM AFB1. The BNF-only diet gave similar, but less dramatic effects (5.9-fold at 16 microM AFB1, 3.5-fold at 512 microM AFB1).(ABSTRACT TRUNCATED AT 250 WORDS)

Aflatoxin B1↗

The Chinese total diet study in 1990. Part I. Chemical contaminants.

The Chinese total diet study in 1990 estimated the dietary intake of 24 chemical contaminants and 72 nutrients from 4 market baskets collected and prepared in 12 provinces. Twelve food group composites were made for each regional market basket. The overall dietary Pb, Cd, Hg, hexachlorocyclohexane HCH, and DDT intakes were well below their corresponding acceptable daily intakes. However, the Pb content of eggs from the 2 southern regions exceeded the tolerance limit. The Hg content of legumes just reached the tolerance limit, and Hg in eggs from the North 1 region exceeded the tolerance limit. The dietary HCH intake has decreased significantly since the 1980s, but dietary DDT intake has decreased rather slowly. Five organophosphorus pesticides were detected out of a total of 12 organophosphorus pesticides analyzed. Among them, methamidophos was the most outstanding. The intake of total committed dose equivalents (CDEs) of the 6 radionuclides was 0.24 mSv/a; only 1.5% was accounted for by 90Sr and 137Cs. 210Pb, 210Po, 226Ra, and 228Ra accounted for 98.5% of the total CDEs. The main food sources of those radionuclides were cereals, vegetables, and aquatic foods. Aflatoxin B1 was detected at very low levels only in the cereal composite of the North 1 region. Aflatoxin M1 was not detected in any of the milk and milk products. The overall results show that there is no significant environmental contamination of the average Chinese diet.

Adult↗

Two-dimensional chromatographic method for determination of aflatoxins in liver; occurrence of aflatoxins in animal liver.

A thin-layer chromatographic method is described for the analysis of aflatoxins in animal liver. Liver samples are extracted with chloroform and phosphoric acid. After filtration, an aliquot is evaporated and defatted by liquid-liquid partitioning. The extract is submitted to silica gel minicolumn cleanup and the final extract is concentrated and submitted to two-dimensional thin-layer chromatography (TLC). The identity of aflatoxins B1 and M1 is confirmed with trifluoroacetic acid (TFA) carried out on the thin-layer plate used for quantitation of these aflatoxins. The method permits the detection and confirmation of aflatoxins in liver in concentrations as low as 0.05 micrograms/kg. Average recoveries for aflatoxin M1 and aflatoxin B1 at spiking levels of 0.2 micrograms/kg were found to be 65% and 85%, respectively. With this method, 73 samples of bovine liver, 70 samples of porcine liver, and 56 samples of chicken liver taken from different slaughterhouses were investigated. In one sample of bovine liver, aflatoxins B1, B2, and M1 could be detected in concentrations of 0.10, 0.03, and 0.08 micrograms/kg, respectively.

Aflatoxin B1↗

A comparison of the effects of pretreatment with phenobarbitone and 3-methylcholanthrene on the metabolism of aflatoxin B1 by rat liver microsomes and isolated hepatocytes in vitro.

In agreement with previous reports (Neal and Colley, Biochem. J., 174 (1978) 839; Gurtoo and Dave, Cancer Res., 35 (1975) 382) the capacity of isolated hepatic microsomes to metabolise aflatoxin B1 (AFB1) is enhanced by pretreatment in vivo with phenobarbitone. Microsomes isolated from rats pretreated with 3-methylcholanthrene also exhibit increased metabolism of AFB1. The levels of metabolism are increased in proportion to the increased levels of cytochromes P-450 and P-448 indicating similar overall efficiencies of the two cytochromes to metabolise AFB1. However, the qualitative aspects of the metabolism induced by the two compounds are very different. In agreement with the previous data (Neal and Colley, Biochem J., 174 (1978) 839) the formation of aflatoxins Q1, M1 and B1-dihydrodiol are enhanced by pretreatment with phenobarbitone whereas pretreatment with 3-methylcholanthrene, while not affecting the production of aflatoxin Q1 and slightly lowering AFB1-dihydrodiol formation, increases the production of aflatoxin M1 greater than 10-fold. Covalent binding of AFB1 to microsomal protein in vitro is increased by pretreatment in vivo with phenobarbitone, but decreased by pretreatment with 3-methylcholanthrene. The changes in the level of protein binding in vitro brought about by these pretreatments are quantitatively similar to the relative changes in AFB1-dihydrodiol tris complex production induced by the two compounds indicating a role for this metabolite in protein binding. Covalent binding of AFB1 to DNA in vitro is also increased by pretreatment in vivo with phenobarbitone, but not by 3-methylcholanthrene and the total level of binding of AFB1 to DNA in the in vitro system is greater than binding to microsomal protein. The possible mechanisms for binding AFB1 to microsomal protein and DNA are discussed. In contrast to the microsomal incubations, only low levels of aflatoxins Q1 and M1 are present after 2 h incubation AFB1 with intact hepatocytes isolated from control, methylcholanthrene or phenobarbitone pretreated rats. Pretreatment with either phenobarbitone or 3-methylcholanthrene induces the formation of polar metabolites, presumably conjugates, emphasising the predominant role of phase 2 metabolism in intact cellular systems.

Aflatoxin B1↗

Fate of aflatoxins in tissues, fluids, and excrements from cows dosed orally with aflatoxin B1.

A study was conducted to determine aflatoxins in tissues and non-tissues of 2 Holstein cows given oral doses of 0.35 mg of purified aflatoxin B1/kg of body weight/day for 3 consecutive days. Cow 1 was slaughtered 24 hours after the 3rd dose, and cow 2, after day 3, was fed aflatoxin-free rations for 7 additional days before slaughter. Tissue samples of brain, gallbladder and bile, heart, intestine, kidney, liver, lung, mammary gland, skeletal muscle, spleen, supramammary lymph nodes, thymus, and tongue, and nontissue samples of blood, feces, milk, rumen content, and urine were examined. Aflatoxins B1 and M1 were found in all samples of cow 1, except the thymus. Kidney, liver, and mammary gland had the highest concentrations of total aflatoxins (57.9, 13.2, and 25.1 ng/g, respectively), with the aflatoxin M1 concentration 40 times more than the aflatoxin B1 level in kidney. Aflatoxin residues were present (0.02 to 0.11 ng/g) only in kidney, liver, and intestine of the tissues from cow 2 (fed aflatoxin-free feed for 7 additional days). Aflatoxin B1 was not present in nontissue samples, but aflatoxin M1 (0.10 and 1.5 ng/ml) was found in the last milk and urine samples from the same cow. Urine assays are a possible way to monitor the presence of aflatoxin residues in meat tissues.

Aflatoxins↗

Immunoaffinity column clean-up for the high-performance liquid chromatographic determination of aflatoxins B1, B2, G1, G2, M1 and Q1 in urine.

A method for the determination of aflatoxins B1, B2, G1, G2, M1 and Q1 in human urine has been developed. The 10-ml urine samples were automatically cleaned up on immunoaffinity columns and analysed by high-performance liquid chromatography (HPLC), including post-column derivatization with bromine and fluorescence detection. Average aflatoxin recoveries were: B1 103%, B2 106%, G1 98% and G2 96% in the range 6.8-73 pg/ml of urine and M1 103% and Q1 100% in the range 18-97 pg/ml of urine. The relative standard deviations were all between 1% and 21%. The determination limits of aflatoxins in urine were 6.8 pg/ml for B1, B2, G1 and G2 and 18 pg/ml for M1 and Q1.

Aflatoxin B1↗

CYP1A induction by beta-naphthoflavone, Aroclor 1254, and 2,3,7,8-tetrachlorodibenzo-p-dioxin and its influence on aflatoxin B1 metabolism and DNA adduction in zebrafish.

This study investigated the inductive response of cytochrome P4501A (CYP1A) in the zebrafish (Danio rerio) following exposure to Aroclor 1254, beta-naphthoflavone (betaNF), and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and then investigated TCDD modulation of aflatoxin B1 (AFB1) metabolism and hepatic AFB1-DNA adduction. Aroclor 1254 fed at 500 ppm for 1 to 9 days or intraperitoneal (ip) injection of 75-200 mg Aroclor 1254/kg body weight failed to induce CYP1A protein or associated 7-ethoxyresorufin-O-deethylase (EROD) activity. By contrast, dietary betaNF at 500 ppm for 3 or 7 days induced CYP1A protein and EROD activity approximately threefold above controls. A single ip injection of 150 mg/kg betaNF showed maximal induction of CYP1A protein and EROD activity near 24 hr, both of which decreased to control levels during the next 6 days. Single ip administration of 25, 50, 100, or 150 mg betaNF/kg body weight provided dose-responsive increases in CYP1A and EROD activity. Dietary exposure to 0.75 ppm TCDD for 3 days also significantly induced CYP1A and EROD. The effect of TCDD on the metabolism of [3H]AFB1 in zebrafish was then investigated. The major [3H]AFB1 metabolites excreted in water over 24 hr in the control group were aflatoxicol, aflatoxicol-glucuronide, and parent AFB1. By contrast, the predominant metabolites in the TCDD-pretreated group were aflatoxicol-M1-glucuronide, aflatoxicol, aflatoxin M1 plus aflatoxicol-M1 (unresolved), aflatoxicol-glucuronide, and parent AFB1. Surprisingly, hepatic AFB1-DNA adduction was approximately fourfold higher in the TCDD treated group than in controls. This significant difference could not be explained by increased capacity for bioactivation of AFB1 as measured by an in vitro AFB1-exo-8, 9-epoxide trapping assay. However, it was demonstrated that both control and induced zebrafish have high capacity to bioactivate aflatoxin M1 to a reactive intermediate, such that secondary bioactivation of this genotoxic intermediate may be responsible for the increased DNA binding.

Aflatoxin B1↗

Aspergillus flavus and aflatoxins B1, B2, and M1 in corn associated with equine death.

Corn from an Arkansas farm, where three horses died and others became sick, was investigated for causative principles. Necropsy of the three horses revealed what appeared to be severe hepatic necrosis. Histopathological examination indicated a pattern of hepatic lesions that was suggestive of aflatoxin contamination of the feed. Mycological examination of the corn by dilution plating revealed 95% of the colonies as Aspergillus flavus. Chemical analysis of the corn for mycotoxins was positive for aflatoxin B1, B2, and M1 at concentrations of 114, 10, and 6 micrograms/Kg, respectively. Cyclopiazonic acid, sterigmatocystin, and the Fusarium toxins, vomitoxin (deoxynivalenol), T-2 toxin, and diacetoxyscirpenol, were not detected. The presence of aflatoxin metabolites in the moldy corn and the presence of appropriate lesions were compatible with the diagnosis, equine aflatoxicosis.

Aflatoxins↗

[Determination of aflatoxins in milk and milk products (author's transl)].

During the period from September 1972 till December 1974 260 samples of milk, 41 of milk powder, 54 of yoghurt, 80 of fresh cheese, 65 of camembert, 77 of hard cheese and 134 of processed cheese were investigated for their contents of aflatoxin B1, B2, G1, G2, and M1. In all products containing toxin only aflatoxin M1 could be detected. The average values of aflatoxin M1 concentration during the period of investigation amounted to: 0.07 microng/1 for milk, 0.50 microng/kg for milk powder, 0.20 microng/kg for yoghurt, 0.23 microng/kg for fresh cheese, 0.43 microng/kg for hard cheese, 0.26 microng/kg for processed cheese, and 0.31 microng/kg for camembert. As maximum values the following concentrations were found: milk 0.33 microng/1, milk powder 2.0 microng/kg, yoghurt 0.47 microng/kg, fresh cheese 0.51 microng/kg, camembert 0.73 microng/kg, hard cheese 1.3 microng/kg, and processed cheese 0.55 microng/kg.

Aflatoxins↗