Disposition and metabolism of radiolabelled pentachloroanisole in rats and rabbits.

Male Sprague-Dawley rats and New Zealand White rabbits were administered 14C-labelled pentachloroanisole (PCA) in corn oil by gavage as single doses of 25 mg/kg and were then placed in individual metabolism cages for as long as 4 days. Peak blood level of radioactivity occurred 6 hr after administration of the dose to rats and between 3 and 4 hr in rabbits; the blood elimination half-life ranged from 8 to 15 hr in rats and averaged 6 hr in rabbits. Rats excreted an average of 54.2% of the administered radiolabel in the urine and 32.4% in the faeces during the 96 hr following the dose; rabbits excreted an average of 84.2 and 13.1% of the radiolabel in the urine and faeces, respectively, during this time. Examination of the metabolites in the rat showed that 60% of the urinary radioactivity was attributable to tetrachlorohydroquinone (TCH), 3% to free pentachlorophenol (PCP) and 29% to conjugated PCP; faecal metabolites were PCP (85.7%), TCH (4.3%) and polar metabolite(s) (10%). In the rabbit, 58% of the urinary radioactivity was attributable to TCH, 8% to free PCP and 34% to conjugated PCP. Faecal metabolites consisted of PCP and conjugated material.

Tissue distribution and excretion of 14C-labelled cinnamic aldehyde following single and multiple oral administration in male Fischer 344 rats.

14C-labelled cinnamic aldehyde (CNMA) was given as a single oral dose, or 24 hr after multiple oral administration of non-radioactive CNMA for 7 days at 24-hr intervals, to male Fischer 344 rats at dose levels of 5, 50 or 500 mg/kg body weight. Residues of radioactive CNMA were measured. After the single dose radioactivity was distributed primarily in the gastro-intestinal tract, the kidneys and the liver of the rats. The radiolabel was excreted mainly in the urine, and at 24 hr 85.1, 84.2 and 81.2% of the administered radiolabel was recovered in the urine at the 5, 50 and 500 mg/kg dose levels, respectively. Faecal excretion of radiolabel at 24 hr for the 5, 50 and 500 mg/kg doses was 5.1, 4.0 and 3.2% of the administered dose, respectively. At all dose levels, a small amount of the dose was distributed to the fat and was easily measured in animals killed 3 days after dosing at the 50 or 500 mg/kg dose levels. Following multiple oral administration, similar tissue distribution and excretion patterns of radiolabel were found at the three dose levels. After 24 hr the administered radiolabel was distributed mainly to the fat, liver and gastro-intestinal tract. At 24 hr, recoveries of the radiolabel in the urine were 80.4, 80.6 and 81.9% of the dose for the 5, 50 and 500 mg/kg dose levels, respectively. Faecal excretion of radiolabel after multiple dosing at 24 hr accounted for 6.3, 6.9 and 4.5% of the administered radioactivity at the 5, 50 and 500 mg/kg dose levels, respectively. The major metabolic pathway of CNMA for all single and the 5 and 50 mg/kg multiple dose levels in this species of rat was found to be degradation to benzoic acid through beta-oxidation and excretion in the urine mainly as hippuric acid, with much smaller amounts of benzoic and cinnamic acids. At the multiple dose level of 500 mg/kg, benzoic acid was the major urinary metabolite, indicating that in the Fischer 344 male rat at this relatively high oral dose level the detoxification of CNMA proceeds differently and an alternative metabolic pathway is proposed.

Time required to achieve homogeneity of test substances added to dog feed.

The homogeneity of test substances in a carrier (animal feed) is a critical factor in conducting long-term feeding studies in laboratory animals. A method for determining the adequate amount of mixing to achieve homogeneity by a mixer of the type described has been determined when 2 distinctly different compounds are added to ground dog feed. Nicotinic acid and butylated hydroxyanisole at a concentration of 1% were separately mixed with the dog feed for 15, 30, 45, 60, and 120 min to determine optimum mixing time. Test portions were taken from 4 different sampling sites at each time period and analyzed in duplicate for the added substance. Four batches were prepared and the results were aggregated. Very little interbatch variability was observed. The variance of the average values from the 4 sampling sites at each time period was calculated and used as a simple, crude, but effective numerical quantity to monitor the approach to homogeneity of the mixture.