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Coincubation of rat renal proximal tubules with hepatic subcellular fractions potentiates the effects of para-aminophenol.

Treatment of rats with para-aminophenol (PAP) (300 mg/kg ip) produced decreases in renal nonprotein sulfhydryl (NPSH) content, oxygen consumption, and adenine nucleotide concentrations 2-4 hr following administration. In contrast, incubation of rat renal tubules with up to 1 mm PAP for 4 hr produced inconsistent changes in renal tubules. This discrepancy suggested that extrarenal metabolism of PAP may be involved in PAP bioactivation and nephrotoxicity. We designed the present studies to test the hypothesis that hepatic metabolism of PAP potentiates the effects of PAP on renal tubules. Incubation of renal tubules with 0.5 mm PAP and 10 mg protein from hepatic postmitochondrial supernatant (S9 fraction) in the absence of glutathione (GSH) for 4 hr did not alter renal oxygen consumption or adenine nucleotide metabolite concentrations. We observed no changes when we incubated tubules with 0.5 mm PAP and 1 mm GSH in the absence of hepatic S9 fraction. However, incubation of renal tubules with 0.5 mm PAP, 1 mm GSH, and 10 mg hepatic S9 protein for 4 hr significantly decreased renal oxygen consumption and adenosine triphosphate and total nucleotide concentrations. These data suggest that the effects of PAP in renal tubules may be potentiated by enzymatic metabolism of PAP, possibly involving oxidation and GSH conjugation. From experiments using hepatic microsomes or cytosol instead of S9 fraction, we found that changes were produced when we incubated tubules with PAP in the presence of hepatic microsomes, but not cytosol. These data suggest that hepatic microsomal metabolism of PAP may contribute to the production of changes in renal tubules in vitro. PAP-induced changes in renal proximal tubules were prevented when we included a beta-nicotinamide adenine dinucleotide phosphate (NADPH) generating system in the incubation medium. The protective effect of NADPH persisted when microsomes were inactivated by incubation with 1-aminobenzotriazole, a cytochrome P450 inhibitor. These data suggest that cytochrome P450-dependent oxidation is not involved in the production or prevention of PAP-induced changes in renal tubules. The enzyme(s) responsible for PAP bioactivation and the mechanism(s) by which NADPH protects renal tubules from PAP-induced decrements in oxygen consumption and adenine nucleotide concentrations are currently unclear.

Adenine Nucleotides↗

Biochemical characterisation of para-aminophenol-induced nephrotoxic lesions in the F344 rat.

The acute biochemical effects of the nephrotoxin p-aminophenol (PAP) were studied in detail using a combination of conventional bioanalytical and 1H-NMR spectroscopic methods. Dosing PAP (25-100 mg/kg) to male F344 rats resulted in a dose-related proximal nephropathy with consequent elevations in urinary enzymes, glucose, and urine total protein as shown by conventional methodology. 1H-NMR spectroscopy at 400 MHz of urine from PAP-treated rats also revealed a characteristic glycosuria, with concomitant amino aciduria. The increased excretion of these compounds indicates functional defects in the proximal tubule and reduced solute reabsorption efficiency. In addition, 1H-NMR urinalysis and conventional enzymatic analysis showed a dose-related lactic aciduria. Other changes detected by 1H-NMR included a dose-related reduction in the excretion of citrate (confirmed by a conventional biochemical method) and an increase in the excretion of acetate. The degree of abnormalities shown by 1H-NMR urinalysis agreed well with histopathological observations and conventional biochemical indices of nephrotoxicity. 1H-NMR urinalysis therefore serves to highlight changes in the excretion of low MW urine components not routinely studied by conventional biochemical analysis.

Amino Acids↗

Nephrotoxicity of aminophenols: effects of 4-dimethylaminophenol on isolated rat kidney tubules.

In isolated rat kidney tubules DMAP was found to inhibit the gluconeogenesis from lactate, pyruvate, or dihydroxyacetone. The ratio DMAP/protein rather than the calculated concentration of DMAP determined the strength of the effect, 20--25 nmoles DMAP/mg protein inhibiting the rate of gluconeogenesis by about 50%. The inhibition was not reversible. Phenacetin, 4-aminophenol and 4-acetamidophenol were much less effective than DMAP in inhibiting gluconeogenesis in isolated rat kidney tubules. DMAP 14C-labeled in the ring was quickly bound to proteins in kidney tubules. A portion of DMAP which did not exceed about 4 nmoles/mg protein, was bound in compounds soluble in perchloric acid. From this portion tris-GS-DMAP was isolated. DMAP diminished the glutathione content of isolated rat kidney tubules. Reduced glutathione added before DMAP prevented the inhibition of gluconeogenesis and diminished the binding of DMAP to proteins. The binding of DMAP required oxygen and was inhibited by carbon monoxide or cyanide. Several enzymes from isolated kidney tubules were found to be inhibited by DMAP doses which inhibited gluconeogenesis. Large DMAP doses also diminished the sums of ATP + ADP + AMP as well as NAD + NADH and NADP + NADPH. This effect corresponded to an increase in nucleotide degradation products and to increased activity of extracellular LDH. The results indicate that the inhibition of gluconeogenesis by DMAP is not due to a specific effect on one enzyme or on membranes but to unspecific reactions with many substances.

Aminophenols↗

Concanavalin A-peroxidase-diaminobenzidine-periodic acid-m-aminophenol-fast black salt K: a method for the dual staining of neutral complex carbohydrates.

A method has been developed for the dual staining of neutral complex carbohydrates in light microscopy. It combines a concanavalin A-peroxidase-diaminobenzidine (Con A-PO-DAB) method with a period acid-m-aminophenol-Fast Black salt K (PA-AP-FBK) sequence. With the combined method it is possible to stain alpha-D-glycosyl and alpha-D-mannosyl residues brown and 1,2-glycol groups of neutral complex carbohydrates blackish purple. The validity of the method has been confirmed with appropriate histochemical controls and enzyme digestions on test tissues.

3,3'-Diaminobenzidine↗

Effects of biliary cannulation and buthionine sulphoximine pretreatment on the nephrotoxicity of para-aminophenol in the Fischer 344 rat.

The effects of a glutathione depletor, buthionine sulphoximine (BSO) and biliary cannulation on the nephrotoxicity of p-aminophenol (PAP) have been investigated in the F344 rat. Pretreatment with BSO completely protected against the nephrotoxicity of a 50 mg/kg dose of PAP, assessed by clinical chemistry, renal histopathology, and 1H-NMR urinalysis. Biliary cannulation partially protects against nephrotoxicity induced by 100 mg/kg PAP. These data suggest that the nephrotoxicity of PAP may be due in part to the formation of a proximate toxic metabolite in the liver which is excreted in the bile, subsequently reabsorbed and transported via the systemic circulation to the kidney where the toxic effects occur.

Aminophenols↗

The nephrotoxicity of p-aminophenol. I. The effect on microsomal cytochromes, glutathione and covalent binding in kidney and liver.

p-Aminophenol administration lowered the microsomal cytochrome P-450 and b5 content and decreased the activity of NADPH cytochrome c reductase in kidney, but not in liver. Kidney GSH was depleted to 29% of the control value at 2 h, and only partly restored (50% of control) at 24 h. Liver GSH was transiently decreased, the lowest levels (77% of control) occurring at 30 min. The maximum level of covalently bound radioactivity was at two hours when 16.8% of the total radioactivity in kidney, 1.5% in liver and 3.6% in plasma was protein bound. At this time 81% of the total radioactivity in kidney and 95% of that in the liver was present in the soluble fraction.

Aminophenols↗

The role of free radicals in p-aminophenol-induced nephrotoxicity: does reduced glutathione have a protective effect?

The role of free radicals in p-aminophenol (PAP)-induced nephrotoxicity and effects of reduced glutathione (GSH) were investigated. We injected PAP in one group of rats and PAP plus GSH in a second group. All parameters were measured in the renal tissue. Superoxide dismutase (SOD) activity in the PAP + GSH group (7.1 +/- 0.36 U/mg protein) was found to be significantly higher than in the control group (4.9 +/- 0.13) (P < 0.001). Catalase (CAT) was found to be significantly low in both groups (P < 0.001 in the PAP group (13.48 +/- 0.85 U/mg protein), P < 0.01 in the PAP + GSH group (18.75 +/- 1.17) as compared to the control group (41.03 +/- 0.93)). Glutathione peroxidase (GPx) in the PAP and PAP + GSH groups was found to be significantly high (P < 0.01 in the PAP group (5.32 +/- 0.033 U/mg protein), P < 0.001 in the PAP + GSH group (6.48 +/- 0.1)) as compared to the control group (2.93 +/- 0.093)). Similarly, glutathione reductase (GSSGR) in the PAP (0.023 +/- 0.002 U/mg protein), and PAP + GSH (0.025 +/- 0.001) groups was found to be significantly high as compared to the control group (0.014 +/- 0.001) (P < 0.001). GSH in the PAP (161.93 +/- 8.3 mg/mg protein) and PAP + GSH (170.7 +/- 4.51) groups were found to be significantly higher than the control group (104.91 +/- 3.0) (P < 0.001). Malondialdehyte (MDA) in the PAP (11.2 +/- 0.62 nmol/mg protein) and PAP + GSH (9.72 +/- 0.46) groups was found to be significantly higher than in the control group (5.54 +/- 0.51)(P < 0.001). Free radicals might have a major role in the PAP-induced nephrotoxicity. GSH increased nephrotoxicity.

Aminophenols↗

Acetaminophen nephrotoxicity in the rat. II. Strain differences in nephrotoxicity and metabolism of p-aminophenol, a metabolite of acetaminophen.

Acetaminophen (APAP) produces renal necrosis restricted to the straight segment of the proximal tubule in Fischer 344 (F344) rats. On the other hand, Sprague-Dawley (SD) rats are extremely resistant to the nephrotoxic effects of APAP. Such strain differences may be due to different susceptibilities to the nephrotoxic metabolite, p-aminophenol (PAP). PAP administration in both strains of rats resulted in a renal lesion indistinguishable from the APAP-induced renal lesion in F344 rats. The PAP-induced renal lesions in F344 rats, however, were generally more severe than those in SD rats. PAP-induced renal functional changes (elevation in blood urea nitrogen and reduction in the accumulation of p-aminohippurate by renal cortical slices) correlated with strain-dependent histopathological changes. Analysis of urinary metabolites over a 24-hr period following PAP administration (200 and 400 mg/kg) indicated that more PAP was excreted as APAP in SD than in F344 rats. Covalent binding of PAP to renal microsomes in vitro was much greater in F344 rats than in SD rats at substrate concentrations less than 5 mM. These results suggest that strain differences in PAP-induced nephrotoxicity may be related to differences in the intrarenal activation of PAP. Furthermore, strain differences in APAP-induced nephrotoxicity may be related to strain differences in the activation of the nephrotoxic metabolite, PAP.

Acetaminophen↗

Genotoxicity of p-aminophenol in somatic and germ line cells of Drosophila melanogaster.

p-Aminophenol (PAP; as a component of, e.g., hair dyes, photographic developers, as adsorbent in gas filters, as a metabolite of various fungicides, pesticides and drugs) has been tested for genotoxicity in Drosophila by means of the sex-linked recessive lethal test (SLRLT) and the somatic mutation and recombination test (SMART) of the wing. While the SLRLT was not significant, the SMART clearly indicated that the compound has genotoxic properties in this in vivo test in agreement with a majority of mammalian short-term tests in vitro and in vivo. The reducing agent dithiothreitol enhanced the genotoxic effects of PAP in the SMART; the reasons for this interaction remain to be elucidated.

Aminophenols↗

Results of teratogenicity testing of m-aminophenol in Sprague-Dawley rats.

meta-Aminophenol (m-AP) was administered in the diet to female Sprague-Dawley rats for a period of at least 90 days at levels of 0.1, 0.25, and 1.0%. In the 0.25% group a significant reduction in body weight was noted, in comparison with control values, and in the 1.0% group a significant reduction in both body weight and food consumption was noted. Ten of the rats in each group were necropsied. Deposition of iron positive pigment in the spleen, liver, and kidney combined with decreased red blood cell count and hemoglobin and increased mean corpuscular volume indicated a hemolytic effect. There were also morphologic changes in the thyroid which were consistent with hyperactivity. The remaining 25 rats in each group were removed from m-AP treatment and immediately mated to untreated males of the same strain. After the mating period the dams again were given m-AP for the duration of gestation. All dams were killed on Day 20 of gestation; one-third of the fetuses were examined for visceral malformations and two-thirds for skeletal malformations and variations. An additional significant reduction in body weight gain was noted during gestation in the 1.0% group as compared to the control group. There were no other adverse dose-related findings demonstrated in the reproduction performance of the dams or in the survival or development of their offspring. Therefore, although maternal toxicity was demonstrated at the highest dose level, there was no evidence of teratogenic or embryofetal toxicity at any dose level tested.

Abnormalities, Drug-Induced↗

Acetaminophen and p-aminophenol nephrotoxicity in aging male Sprague-Dawley and Fischer 344 rats.

Strain differences in susceptibility of rats to acetaminophen (APAP)-induced nephrotoxicity have been reported previously. Young adult male Fischer 344 (F344) rats are susceptible, whereas weight-matched Sprague-Dawley (SD) rats are not susceptible to APAP nephrotoxicity. Susceptibility to APAP nephrotoxicity is also age dependent, at least in F344 rats. Middle-aged (12-15 months old) male F344 rats are more susceptible to APAP-induced nephrotoxicity than are young adult (2-4 months old) males. APAP nephrotoxicity in aging SD rats has not been evaluated. The present studies were designed to define strain differences in the nephrotoxicity of APAP and p-aminophenol (PAP), a nephrotoxic metabolite of APAP, using 2-, 3-, and 9- to 12-month-old F344 and SD rats. At 2 months of age, F344, but not SD, rats were susceptible to APAP-induced nephrotoxicity. However, at 3 months of age, strain differences were less marked, as susceptibility to APAP nephrotoxicity appeared to increase between 2 and 3 months of age only in SD rats. By 9-12 months of age, susceptibility to APAP nephrotoxicity was comparable in F344 and SD rats. No age- or strain-related differences were observed in the excretory pattern of urinary APAP and metabolites that might explain the increased susceptibility of aging rats to APAP nephrotoxicity. Strain differences in age-matched rats were not marked for PAP-induced nephrotoxicity. Susceptibility of both 3- and 12-month-old F344 and SD rats to PAP-induced nephrotoxicity was greater compared to strain-matched 2-month-old rats. In both F344 and SD rats, PAP nephrotoxicity increased only modestly between 3 and 12 months of age, indicating that increased susceptibility to PAP probably does not play a major role in the age-dependent increase in APAP nephrotoxicity. Thus, strain differences in APAP nephrotoxicity decrease with advancing age. The mechanisms mediating the increased susceptibility to APAP nephrotoxicity in middle-aged rats are not known but may relate, at least in part, to age-dependent differences in pharmacokinetics. The present study highlights the importance of considering the age of rats when evaluating drug toxicity. Even in young adult rats, subtle maturational changes in drug metabolism and/or disposition may occur, making toxicological evaluation in weight-matched rats of different strains and ages inappropriate.

Acetaminophen↗

The toxicity of p-aminophenol in the Sprague-Dawley rat: effects on growth, reproduction and foetal development.

p-Aminophenol (p-AP) was fed in the diet to groups of 40 male and 45 female Sprague-Dawley rats at levels of 0.07, 0.2 or 0.7% for up to 6 months. Methaemoglobin levels were determined after 6 wk. During wk 12, urine was collected from ten rats/sex/group for evaluation of mutagenicity in the Ames test. Clinical chemistry, haematology and histopathology studies were performed in subgroups after 13 and 27 wk. In addition, after 13 wk, 25 females/group were mated to untreated males in a teratology study. After 20 wk, 20 males/group were removed from the test diets and mated to untreated virgin females in a dominant lethal mutagenicity study. These males remained untreated until they were killed at 27 wk. Rats that had been maintained on the test diets throughout the study were also killed at wk 27. The high dose level of 0.7% p-AP resulted in a significant (10-15%) reduction in body-weight gain in both sexes. There was no increase in the level of methaemoglobin and, other than slight reductions in total erythrocytes and haemoglobin in female rats at 13 wk, there were no toxicologically important differences between groups in haematology or clinical chemistry values at any time during the 27 wk of treatment. Dose-related nephrosis was seen in both sexes after 13 and 27 wk and in the high-dose males that were removed from the test diet for a 7-wk recovery period. The compound was not teratogenic, but an increase in developmental variations associated with maternal toxicity was noted at the mid- and high-dose levels. In the dominant lethal study, an increase in the total number of resorptions (but not litters with resorptions) was observed in the high-dose group in the first of two matings but this observation was not confirmed in a follow-up study. Mutagenic activity was not detected in the urine of rats fed p-AP.

Abnormalities, Drug-Induced↗

An amperometric glucose biosensor based on poly(o-aminophenol) and Prussian blue films at platinum electrode.

Prussian blue (PB), as a good catalyst for the reduction of hydrogen peroxide, has been combined with nonconducting poly(o-aminophenol) (POAP) film to assemble glucose biosensor. Compared with PB-modified enzymatic biosensor, the biosensor based on glucose oxidase immobilized in POAP film at PB-modified electrode shows much improved stability (78% remains after 30 days) in neutral medium. Additionally, the biosensor, at an applied potential of 0.0 V, exhibits other good characteristics, such as relative low detection limit (0.01 mM), short response time (within 5s), large current density (0.28 mA/cm2), high sensitivity (24 mAM(-1)cm(-2)), and good antiinterferent ability. The apparent activation energy of enzyme-catalyzed reaction and apparent Michaelis-Menten constant are 34.2 KJmol(-1) and 10.5 mM, respectively. In addition, effects of temperature, applied potential used in the determination, pH value of the detection solution, and electroactive interferents on the amperometric response of the sensor were investigated and are discussed.

Aminophenols↗

An amperometric hydrogen peroxide sensor based on immobilization of hemoglobin in poly(o-aminophenol) film at iron-cobalt hexacyanoferrate-modified gold electrode.

A series of hybrid iron-cobalt hexacyanoferrate (FeCoHCF) films were electrodeposited on gold electrodes from solutions containing 6mM Fe(CN)(6)(3-) with different concentrations of Co(2+) and Fe(3+). FeCoHCF films deposited from solutions with different molar ratios of iron were studied by cyclic voltammetry, and their solid states were characterized by Fourier transform infrared spectroscopy. The kind of FeCoHCF film that deposited from a solution with a molar ratio of iron of 0.4 showed the largest response current to H(2)O(2) and was characterized by energy-dispersive X-ray spectroscopy. Therefore, the optimized FeCoHCF film was combined with nonconducting poly(o-aminophenol) (POAP) film that entrapped the hemoglobin (Hb) to construct hydrogen peroxide biosensor. The response current of the Hb/POAP/FeCoHCF/Au electrode (29.8 nA) was nearly 40 and was 1.5 times that of the Hb/POAP/Au (0.7 nA) and POAP/FeCoHCF/Au (20 nA) electrodes, respectively. The Michaelis-Menten constant of Hb in the Hb/POAP/FeCoHCF/Au film was 9.31 mM. These results show that the immobilized Hb in the Hb/POAP/FeCoHCF/Au film exhibits higher catalytic activity and larger response current to H(2)O(2) by the mediation of FeCoHCF. In addition, effects of applied potential, solution pH, and electroactive interferent on the response current of the Hb/POAP/FeCoHCF/Au electrode were investigated in detail.

Aminophenols↗

Interaction of mushroom tyrosinase with aromatic amines, o-diamines and o-aminophenols.

3-Amino-L-tyrosine was found to be a substrate of mushroom tyrosinase, contrary to what had previously been reported in the literature. A series of amino derivatives of benzoic acid were tested as substrates and inhibitors of the enzyme. 3-Amino-4-hydroxybenzoic acid, 4-amino-3-hydroxybenzoic acid and 3,4-diaminobenzoic acid were oxidized by this enzyme, as previously reported for Neurospora crassa tyrosinase, but 4-aminobenzoic acid and 3-aminobenzoic acid were not. Interestingly, 3-amino-4-hydroxybenzoic acid was oxidized five times faster than 4-amino-3-hydroxybenzoic acid, confirming the importance of proton transfer from the hydroxyl group at C-4 position. All compounds inhibited the monophenolase activity but their effect on the diphenolase activity was small or negligible. 3-Amino-4-hydroxybenzoic acid was a stronger inhibitor than 4-amino-3-hydroxybenzoic acid, indicating their different binding affinity to the oxy form of the enzyme. Both, however, were weaker inhibitors than 3-amino-L-tyrosine, 4-methoxy-o-phenylenediamine and 3,4-diaminobenzoic acid, which was the strongest inhibitor from among the compounds tested. These results show that the relative positioning of the amino group and the hydroxy group in o-aminophenols with respect to the side chain is important both for binding to the dicopper center and for catalysis.

Agaricales↗

Catechol sensor using poly(aniline-co-o-aminophenol) as an electron transfer mediator.

In this work, poly(aniline-co-o-aminophenol) (copolymer) was used as an electron transfer mediator in the electrochemical oxidation of catechol due to its reversible redox over a wide range of pH. The experimental results indicate that the anodic peak potential of catechol at the copolymer electrode is lower than that at the platinum electrode in a solution consisting of catechol and sodium sulfate with pH 5.0, and the activation energy for the electrochemical oxidation of catechol at the copolymer electrode is low (23.6 kJ mol(-1)). These are strong evidence for the electrocatalytic oxidation of catechol at the copolymer electrode. The -OH group on the copolymer chain plays an important role in the electron transfer between the copolymer electrode and catechol in the solution. Based on the catalytic oxidation, the copolymer is used as a sensor to determine the concentration of catechol. The response current of the sensor depends on the concentration of catechol, pH, applied potential and temperature. At 0.55 V (versus saturated calomel reference electrode (SCE)) and pH 5.0, the sensor has a fast response (about 10s) to catechol and good operational stability. The sensor shows a linear response range between 5 and 80 microM catechol with a correlation coefficient of 0.997. It was found that phenol and resorcinol cannot be oxidized at the copolymer electrode at potentials < or =0.55 V, so controlling the sensor potential affords a good way of avoiding the effect of phenol and resorcinol on the determination of catechol.

Aminophenols↗

Synthesis and biological evaluation of copper (II) complexes of sterically hindered o-aminophenol derivatives as antimicrobial agents.

Cu(II) complexes with 4,6-di(tert-butyl)-2-aminophenol (I) and 2-anilino-4,6-di(tert-butyl)phenol (II) have been synthesized and characterized by means of elemental analysis, TG/DTA, FT-IR, UV-vis, ESR, and conductance measurements. The compounds I and II can coordinate in their singly deprotonated forms and behave as bidentate O,N-coordinated ligands; their CuL(2) complexes are characterized by CuN(2)O(2) coordination modes and square planar geometry. In vitro antimicrobial screening against Gram-positive and Gram-negative bacteria, yeasts, and moulds indicated that the compound I and its Cu(II) complex were more active than Questiomycin B, the compound II, and its Cu(II) complex.

Aminophenols↗

Plasma/blood pharmacokinetics and metabolism after dermal exposure to para-aminophenol or para-phenylenediamine.

The pharmacokinetics and metabolism following dermal application of [(14)C]-para-aminophenol (PAP) or [(14)C]-para-phenylenediamine (PPD) were investigated. Groups of rats were treated under occlusion for 24 h with 12.5 mg/kg [(14)C]-PAP, or for 4h with 50 mg/kg [(14)C]-PPD on 10% or 20% of their body surface area, respectively. A female minipig was also treated dermally (24 h, occlusion) with 4.7 mg/kg [(14)C]-PAP on 10% of its body surface area. Blood and plasma samples were analysed for radioactivity and presence of metabolites. In PAP-treated rats, mean plasma levels at 0.5, 1, 2, 4, 8 or 24h were 0.16, 0.24, 0.38, 0.50, 0.36 or 0.14 microg [(14)C]-PAP equivalents/ml, respectively. The plasma half-life was 5.95 h, the C(max) was 0.5 microg/ml, the t(max) was 4 h, and the AUC(0-infinity) was 9.27 microg-equivalentsh/ml. No free PAP was detected in the plasma, but 3 metabolites (M1, M2 and M3) were found in 2-, 4- or 8-h samples at ranges from 0% to 17.7% (M1), 27.6% to 45.0% (M2) or 46.9% to 70% (M3) of the total plasma radioactivity. M2 was identified as acetylated PAP (paracetamol, acetaminophen, APAP), whereas M1 and M3 were identified as O-glucuronide or O-sulfate conjugates of APAP, respectively. In the pig, very low levels of radioactivity (C(max) of approximately 10 ng/ml) were found in the blood, and identified as APAP. Analysis of plasma of PPD-treated rats at 4 h after topical treatment revealed levels of 1.41 +/- 0.34 microg/ml [(14)C]-PPD-equivalents in males, and 7.40 +/- 1.83 microg/ml in females. Radioactivity, reflected a single metabolite, which was identified to be N,N'-diacetylated PPD. Comparison of the plasma APAP levels in rats or the pig following topical PAP with corresponding human plasma levels after a single oral therapeutic dose of APAP suggested a substantial margin of safety. Overall, the results suggest that topically applied PAP or PPD are metabolised in the skin, presumably by N-acetyltransferase-1 resulting in systemic exposure to acetylated metabolites, and not to their parent arylamines.

Absorption↗