HPLC-hrTOF-MS study of copper chlorophylls: Composition of food colorants and biochemistry after ingestion

Despite the daily consumption of copper chlorophylls (E-141i), the green food colorants in foods high in fats, there is a general need for knowledge regarding their exact composition. Consequently, we have analyzed by HPLC-ESI(+)/APCI(+)-hrTOF-MS² the accurate composition of different commercial copper chlorophyll colorants for the first time. Data showed a favored yield of copper pheophytins from a series, while pheophytins from b series are preferentially no complexed with copper. The copper pheophytins present in the food colorants consisted mainly of three structural rearrangements. New fragmentation patterns and structural assignments have been described for several copper pheophytins. During the ingestion of copper chlorophylls, no chlorophyll derivative was present in serum nor urine except a new copper-pyroporphyrin a accumulated in a few livers. In any case, this green additive could represent the ideal food colorant, as most of the copper pheophytins are excreted in the feces showing almost no absorption of copper-chlorophylls compounds.

Pharmacokinetics of Rhodamine 110 and Its Organ Distribution in Rats

Rhodamine dyes have been banned as food additives due to their potential tumorigenicity. Rhodamine 110 is illegal as a food additive, although its pharmacokinetics have not been characterized, and no accurate bioanalytical methods are available to quantify rhodamine 110. The aim of this study was to develop and validate a fast, stable, and sensitive method to quantify rhodamine 110 using high-performance liquid chromatography coupled to tandem mass spectrometry (HPLC-MS/MS) to assess its pharmacokinetics and organ distribution in awake rats. Rhodamine 110 exhibited linear pharmacokinetics and slow elimination after oral administration. Furthermore, its oral bioavailability was approximately 34-35%. The distribution in the liver and kidney suggests that these organs are primarily responsible for rhodamine 110 metabolism and elimination. Our investigation describes the pharmacokinetics and a quantification method for rhodamine 110, improving our understanding of the food safety of rhodamine dyes.

Pharmacokinetics and Biodistribution of the Illegal Food Colorant Rhodamine B in Rats

The International Agency for Research on Cancer (IARC) demonstrated rhodamine B as a potential carcinogen in 1978. Nevertheless, rhodamine B has been illegally used as a colorant in food in many countries. Few pharmacokinetic and toxicological investigations have been performed since the first pharmacokinetic study on rhodamine B in 1961. The aims of this study were to develop a simple and sensitive high-performance liquid chromatography method with fluorescence detection for the quantitative detection of rhodamine B in the plasma and organs of rats and to estimate its pharmacokinetics and biodistribution. The results demonstrated that the oral bioavailabilities of rhodamine B were 28.3 and 9.8% for the low-dose and high-dose exposures, respectively. Furthermore, rhodamine B was highly accumulated in the liver and, to a lesser extent, the kidney, but was undetectable in the brain. These results provide useful information for improving the pharmacokinetics and biodistribution of rhodamine B, supporting additional food safety evaluations.

Intraperitoneal and dietary administration of astaxanthin in rainbow trout (Oncorhynchus mykiss) — Plasma uptake and tissue distribution of geometrical E/Z isomers

Astaxanthin enters circulation in salmonid fishes upon intraperitoneal injection (IP) of small doses. Blood uptake and tissue distribution of geometrical E/Z astaxanthin isomers were determined in tissues and plasma of duplicated groups of rainbow trout (Oncorhynchus mykiss, initial weight 550 g) some of which were administered high doses of astaxanthin by IP in a trial lasting for 8 weeks. Doses of 10 (IP10), 50 (IP50) or 100 mg (IP100) astaxanthin (Lucantin Pink, BASF, Germany), respectively, dispersed in phosphate buffered saline were tested in comparison with diets containing 10 (Control) or 60 (Fed 60) mg astaxanthin kg(-1). Astaxanthin concentrations in all examined tissues and plasma were significantly higher in IP50 and IP100 than in controls and Fed 60 (p<0.05). In IP50, 11 mg astaxanthin kg(-1) muscle was detected after 4 weeks, compared to 4 mg kg(-1) in rainbow trout fed 60 mg kg(-1). Concentrations up to 80 and 100 mg astaxanthin kg(-1) were detected in liver and kidney after IP, respectively, whereas fish only fed astaxanthin contained about 2 mg astaxanthin kg(-1). No increase in muscle astaxanthin concentration was found between 4 and 8 weeks in fish given IP, and the muscle astaxanthin concentration in IP50 and IP100 were similar. Muscle concentration and injected dose were curvilinearly correlated and the proportion of ingested dose retained by the muscle was negatively correlated with the amount of injected astaxanthin. Plasma and muscle concentrations of astaxanthin were highly correlated (p<0.0001). Astaxanthin Z-isomers accumulated selectively in the various tissues after IP, whereas all-E-astaxanthin was preferably absorbed into plasma when administered via the diet. There was a selective uptake of all-E-astaxanthin in the muscle of all fish. Mortality was not affected by treatment, but a dose-dependent reduction in SGR was evident after IP. In conclusion, a more rapid and higher uptake of astaxanthin in plasma, muscle, kidney and liver of rainbow trout takes place after IP compared to when astaxanthin is fed via the diet.

[Green urine. A case report and review of the literature]

Green urine, a well described condition, can be caused by a variety of agents. Here we describe a case of green urine caused by blue food colouring during tube feeding. In the article, we list more than 20 drugs, chemical agents and microorganisms which have been associated with green urine.

Bio-metabolic disposition of metanil yellow, orange II and their blend by caecal microflora of rats

Caecal microflora were employed to study the degradation pattern, with time course of Metanil yellow and Orange II-two extensively used non-permitted food colours. Metanil yellow and Orange II showed the respective Degradation Index 50 (DI 50) values of 369 and 288 min. However, the blend of Metanil yellow and Orange II (1:1) resulted in the D1 50.value of 288 min. Metanil yellow, Orange II and their blend were resolved into respective metabolites in different solvent systems.

Absorption, distribution and excretion of the colour fraction of Caramel Colour IV in the rat

Caramel Colour IV prepared from [U-14C]glucose was ultrafiltered in order to isolate the high molecular weight colour fraction (HMCF). The colour fraction that was non-permeable to a 10,000-Da porosity membrane, contained 84% of the colour, 22% of the solids and 24% of the radioactivity of the [14C]Caramel Colour IV. The absorption, distribution and excretion of [14C]HMCF were evaluated in male rats after administration of single or multiple oral doses of the material at a dosage level of 2.5 g/kg body weight. Rats on the multiple oral dosage regimen were given unlabelled HMCF in their drinking water for 13 days before the administration of a bolus dose of [14C]HMCF on day 14. On both dosage regimens, the predominant route of excretion was by way of the faeces. Less than 3% of the administered radioactivity was excreted in the urine and only a negligible amount was found in the expired air. More than 99% of the administered radioactivity was excreted within 96 hr. The principal tissues in which radioactivity was found were the mesenteric lymph nodes, liver, kidney and tissues of the gastro-intestinal tract. No major differences were observed in the absorption, distribution or excretion patterns between the single and multiple oral dose regimens.

Pharmacokinetic data in the evaluation of the safety of food and color additives

Safety evaluation of food and color additives intended for human use is usually based on toxicity data obtained from animal studies; human data are rarely available. The extrapolation of animal data to humans is often controversial. The important role that pharmacokinetic data could play in the safety evaluation of food and color additives is now widely recognized. This paper reviews the current scientific knowledge concerning the application of properly designed pharmacokinetic studies to the evaluation of the safety of food and color additives. In principle, pharmacokinetic data can be useful not only in designing, interpreting, and extrapolating animal toxicity studies to humans, but also in providing insight into the mechanisms of toxicity. Examples of such applications are provided.

Evaluating the safety of food and color additives with pharmacokinetic data

Pharmacokinetic studies are designed to quantify, as a function of time, the processes associated with absorption, distribution, metabolism, and excretion of a chemical in experimental animals or in humans. Such studies have played an important role in drug safety evaluation and could be very useful in the safety evaluation of food and color additives. This presentation provides an overview of the potential use of metabolic and pharmacokinetic data in the design and evaluation of toxicological studies and in the assessment of the potential hazard to humans from exposure to food or color additives.

Effect of oral and parenteral administration of B6 vitamers on the lymphopenia produced by feeding ammonia caramel or 2-acetyl-4(5)-(1,2,3,4-tetrahydroxy)butylimidazole to rats

The ability of B6 vitamers to prevent the lymphopenic effects of ammonia caramel fed to rats has been evaluated. Diets containing 10 ppm pyridoxine or pyridoxal prevented the lymphopenia produced in rats consuming an 8% (w/v) solution of ammonia caramel, whereas the dietary content of pyridoxamine needed to be increased to 20 ppm to have the same effect. In contrast to the results of the enteral administration of the individual B6 vitamers, pyridoxamine was found to be the most effective vitamer in preventing the ammonia caramel-induced lymphopenia when administered parenterally. However, all the nutritionally active forms of vitamin B6 were able to prevent the depression of the peripheral blood lymphocyte count, which resulted from ingestion of ammonia caramel by rats. The proposal that oral administration of pyridoxine may prevent the intestinal absorption of the lymphopenic constituent of ammonia caramel, 2-acetyl-4(5)-(1,2,3,4-tetrahydroxy)butylimidazole (THI), is discredited, since THI was found to reduce the lymphocyte count after parenteral administration in rats fed 0.04 ppm pyridoxone in the diet and that increased amounts of dietary pyridoxine (10 ppm) could still prevent this effect. These findings further emphasise the important relationship between dietary vitamin B6 content and the lymphopenic effects of ammonia caramel/THI in the rat.

Metabolic disposition of 14C-labelled carmoisine in the rat, mouse and guinea-pig

The absorption, metabolism and excretion of 14C-labelled carmoisine has been studied in the rat, mouse and guinea-pig. Following administration of a single oral dose of either 0.5 or 50 mg/kg body weight, substantially all of the dose was recovered in the excreta within 72 hr, mainly in the faeces. Although the urinary excretion of radioactivity was similar in the rat and the mouse, the proportion of the radioactivity found in the urine of the guinea-pig was significantly greater than that of the other species at both dose levels. Pretreating male rats with unlabelled colouring in the diet (0.05%, w/w) for 28 days prior to dosing with 14C-labelled colouring had no effect on the route of excretion or the time taken to eliminate the majority of the labelled dose. Following a single oral dose of 14C-labelled colouring to previously untreated rats, mice and guinea-pigs or to rats pretreated as above, no marked accumulation of radioactivity in any tissue was found. Pregnant rats eliminated a single oral dose of 14C-labelled colouring at a similar rate to non-pregnant females, and the concentration of radioactivity in the foetuses was similar to that in the other tissues. Naphthionic acid was the major urinary metabolite in all three species. In the rat and mouse, most of the remaining radioactivity co-chromatographed with 2-amino-1-naphthol-4-sulphonic acid (2-ANS), but in the guinea-pig radioactivity also co-chromatographed with 1,2-naphthoquinone-4-sulphonate (1,2-NQS). Only a trace amount of unchanged carmoisine was detected in the urine of the species examined. Naphthionic acid was also found in the faeces of all three species, but neither carmoisine, 2-ANS or 1,2-NQS was detected. At least five other radioactive metabolites were found in the faecal extracts of all three species, including a substantial amount of a compound with chromatographic properties similar to those of a trace metabolite in the urine. Two of the faecal metabolites were hydrolysed by beta-glucuronidase and sulphatase treatment. In studies on the absorption of carmoisine at concentrations of 50, 500 or 5000 ppm from isolated intestinal loops, no significant absorption was detected in the rat, mouse or guinea-pig.

Metabolic disposition of 14C-labelled amaranth in the rat, mouse and guinea-pig

The absorption, metabolism and excretion of orally administered 14C-labelled amaranth has been studied in the rat, mouse and guinea-pig. Following administration of a single oral dose of either 2 or 200 mg/kg, most of the radioactivity was excreted in the urine and faeces in the first 24 hr, and substantially all of the dose was recovered in the excreta within 72 hr. In the rat and mouse, the principal route of excretion was the faeces, whereas in the guinea-pig, urinary excretion accounted for up to 50% of the dose. In the rat and guinea-pig the proportion of the dose excreted in the urine was significantly greater at the lower dose level. No marked accumulation of radioactivity was found in any tissues 72 hr after the administration of the labelled colouring. For all three species most of the radioactivity was shown to be associated with naphthionic acid, with traces of unchanged amaranth and a number of other unidentified metabolites also being detected. In the rat and mouse substantially all of the remaining radioactivity was associated with a single unidentified component. Naphthionic acid was found in the faeces of all three species along with a substantial, but variable, amount of unchanged dye. At least six other radioactive peaks were seen in the chromatograms of faecal extracts; two of these peaks had similar chromatographic properties to the unknown metabolites in the urine, but there was no peak corresponding to 1-amino-2-naphthol-3,6-disulphonic acid (1-ANDSA), previously reported as a urinary metabolite of amaranth. In studies of absorption from isolated loops of small intestine of the rat, mouse and guinea-pig, no significant absorption of amaranth was detected over a 100-fold concentration range (20-2000 ppm).

Metabolic disposition of 14C-labelled Brown HT in the rat, mouse and guinea-pig

The absorption, metabolism, tissue distribution and excretion of 14C-labelled Brown HT has been studied in the rat, mouse and guinea-pig. Following administration of a single oral dose of either 50 or 250 mg Brown HT/kg, substantially all of the dose was excreted in the urine and faeces within 72 hr, with the majority (more than 80%) being accounted for in the faeces. A significant difference in urinary excretion of radioactivity was seen between male and female rats, as well as clear species differences at the two dose levels used. In all species studied, naphthionic acid was the major urinary metabolite, whereas in the faeces naphthionic acid, trace quantities of unchanged dye and at least two unidentified metabolites were found. Pregnant rats eliminated a single oral dose of 14C-labelled colouring at a rate similar to that in non-pregnant females, but some retention of radioactivity was found in the foetuses. Radioactivity was present in all tissues of male rats 24 hr after an oral dose of 250 mg 14C-labelled Brown HT/kg, with the highest concentrations in the gastro-intestinal tract, kidney and lymph nodes. Clearance from the gastro-intestinal tract was more rapid than from other tissues, but by day 7, the concentration of radioactivity (less than 0.001% of the dose/g) was similar in all tissues except the kidney and mesenteric lymph nodes. Similar results were obtained with animals pretreated for 21 days with either unlabelled or 14C-labelled Brown HT (250 mg/kg/day) prior to a radioactive dose. For most tissues examined, the concentration of radioactivity was greater with pretreatment than without. These results suggest that despite the rapid reduction and elimination of the major part of an oral dose of Brown HT, some colouring and/or metabolites accumulate in most tissues of male rats during repeated daily administration, but that only in the kidney and mesenteric lymph nodes is the accumulation tissue-specific. The accumulated radioactivity is cleared rapidly from most tissues on cessation of treatment. No significant absorption of either Brown HT, metabolites or subsidiary dyes was detected using isolated loops of small intestine.