Absorption, disposition and metabolism of di-isononyl phthalate (DINP) in F-344 rats.

Di-isononyl phthalate (DINP; CAS no. 68515-48-0) is a general-purpose plasticizer for polyvinyl chloride. It produced liver and kidney effects when given to rodents at high oral doses, but there were no target organ effects in primates treated under similar conditions. To assist in understanding the basis for these species differences, the pharmacokinetic properties of DINP were evaluated in rodents following both oral and dermal administration. These studies demonstrated that the pharmacokinetic properties of DINP are similar to those of other high-molecular-weight phthalates. When orally administered to rodents, DINP is rapidly metabolized in the gastrointestinal tract to the corresponding monoester, absorbed and excreted, primarily in the urine. Shortly after administration, DINP is found primarily in liver and kidneys, but it does not persist or accumulate in any organ or tissue. It is very poorly absorbed from the skin, but once absorbed it behaves in the same way as the orally administered material. The results of these rodent studies contrast with data from studies involving humans or other primates, which indicate low absorption at low oral doses and much more limited total absorption at high doses. It appears that many, if not all, of the effects of DINP in rodent studies are associated with internal doses that would be difficult, if not impossible, to achieve in humans under any circumstances. Thus, the results of rodent studies may not be very useful in assessing the potential risks to humans from high-molecular-weight phthalates.

Reversibility and persistence of di-2-ethylhexyl phthalate (DEHP)- and phenobarbital-induced hepatocellular changes in rodents.

The tumor promotion stage of chemical carcinogenesis has been shown to exhibit a persistence of cellular effects during treatment and the reversibility of these changes upon cessation of treatment. Inhibition of gap-junctional intercellular communication and increased replicative DNA synthesis appear to be important in this process. The present study assessed the persistence and reversibility of gap-junctional intercellular communication inhibition, peroxisomal proliferation, and replicative DNA synthesis in livers from male F344 rats and B6C3F1 mice. Dietary administration of 20,000 mg/kg DEHP to male rats for 2 weeks decreased intercellular communication (67% of control) and enhanced replicative DNA synthesis (4.8-fold over control). Elevation of the relative liver weight and the induction of peroxisomal beta oxidation were also observed following treatment with 20,000 mg/Kg DEHP for 2 weeks. Following DEHP administration at a dose of 6000 mg/kg for 18 months, inhibition of gap-junctional intercellular communication persisted, and the relative liver weight and induction of peroxisomal beta oxidation remained elevated in both rats and male B6C3F1 mice. Treatment of rats and mice with phenobarbital for 18 months (500-mg/kg diet) also produced an increase in relative liver weight and a decrease in cell-to-cell communication. In recovery studies in which DEHP was administered to male F344 rats for 2 weeks and then withdrawn, the relative liver weight, rate of peroxisomal beta oxidation, increase in replicative DNA synthesis, and inhibition of gap-junctional intercellular communication returned to control values within 2 to 4 weeks after DEHP treatment ceased. Recovery studies with phenobarbital produced similar results. The primary active metabolite of DEHP, mono-2-ethylhexyl phthalate (MEHP), was detected in the livers of animals treated with DEHP for greater than 2 weeks. However, it could not be detected after removal of DEHP from the diet for 2 weeks. This study demonstrated that inhibition of gap-junctional intercellular communication, along with indicators of peroxisomal proliferation, including increased relative liver weight and enhanced peroxisomal beta oxidation, persist while DEHP treatment continues but reverses when treatment is stopped. Studies with phenobarbital produced a similar pattern of response.

Effects of Di-2-ethylhexyl phthalate (DEHP) on gap-junctional intercellular communication (GJIC), DNA synthesis, and peroxisomal beta oxidation (PBOX) in rat, mouse, and hamster liver.

The present study evaluated the effect of di-2-ethylhexyl phthalate (DEHP) on gap-junctional intercellular communication (GJIC), peroxisomal beta-oxidation (PBOX) activity, and replicative DNA synthesis in several rodent species with differing susceptibilities to peroxisome proliferator-induced hepatic tumorigenesis. A low (non-tumorigenic) and high (tumorigenic) dietary concentration of DEHP was administered to male F344 rats for 1, 2, 4, and 6 weeks. Additionally, a previously non-tumorigenic dose (1000 ppm) and tumorigenic dose of DEHP (12,000 ppm), as determined by chronic bioassay data, were examined following 2 weeks dietary administration. Male B6C3F1 mice were fed the non-tumorigenic concentration, 500 ppm, and the tumorigenic concentration, 6000 ppm, of DEHP for two and four weeks. The hepatic effects of low and high concentrations of DEHP, 1000 and 6000 ppm, were also examined in male Syrian Golden hamsters (refractory to peroxisome proliferator-induced tumorigenicity). In rat and mouse liver, a concentration-dependent increase in the relative liver weight, PBOX activity, and replicative DNA synthesis was observed at the earliest time point examined. Concurrent to these observations was an inhibition of GJIC. In hamster liver, a slight increase in the relative liver weight, PBOX activity, and replicative DNA synthesis was observed. However, these effects were not of the same magnitude or consistency as those observed in rats or mice. Furthermore, DEHP had no effect on GJIC in hamster liver at any of the time points examined (2 and 4 weeks). HPLC analysis of DEHP and its primary metabolites, mono-2-ethylhexyl phthalate (MEHP), and phthalate acid (PA), indicated a time- and concentration-dependent increase in the hepatic concentration of MEHP. At equivalent dietary concentrations and time points, the presence of MEHP, the primary metabolite responsible for the hepatic effects of DEHP, demonstrated a species-specific response. The largest increase in the hepatic concentration of MEHP was observed in mice, which was greater than the concentration observed in rats. The hepatic concentration of MEHP was lowest in hamsters. Hepatic concentrations of DEHP and phthalic acid were minimal and did not correlate with concentration and time. Collectively, these data demonstrate the inhibition of hepatic GJIC and increased replicative DNA synthesis correlated with the observed dose- and species-specific tumorigenicity of DEHP and may be predictive indicators of the nongenotoxic carcinogenic potential of phthalate esters.

Effects of di-isononyl phthalate, di-2-ethylhexyl phthalate, and clofibrate in cynomolgus monkeys.

The effects of the peroxisome proliferators di-isononyl phthalate (DINP) and di-2-ethylhexyl phthalate (DEHP) were evaluated in young adult male cynomolgus monkeys after 14 days of treatment, with emphasis on detecting hepatic and other effects seen in rats and mice after treatment with high doses of phthalates. Groups of 4 monkeys received DINP (500 mg/kg/day), DEHP (500 mg/kg/day), or vehicle (0.5% methyl cellulose, 10 ml/kg) by intragastric intubation for 14 consecutive days. Clofibrate (250 mg/kg/day), a hypolipidemic drug used for cholesterol reduction in human patients was used as a reference substance. None of the test substances had any effect on body weight or liver weights. Histopathological examination of tissues from these animals revealed no distinctive treatment-related effects in the liver, kidney, or testes. There were also no changes in any of the hepatic markers for peroxisomal proliferation, including peroxisomal beta-oxidation (PBOX) or replicative DNA synthesis. Additionally, in situ dye transfer studies using fresh liver slices revealed that DINP, DEHP, and clofibrate had no effect on gap junctional intercellular communication (GJIC). None of the test substances produced any toxicologically important changes in urinalysis, hematology, or clinical chemistry; however, clofibrate produced some emesis, small increases in serum triglyceride, decreased calcium, and decreased weights of testes/epididymides and thyroid/parathyroid. The toxicological significance of these small changes is questionable. The absence of observable hepatic effects in monkeys at doses that produce hepatic effects in rodents suggests that DINP, DEHP, and clofibrate would also not elicit in primates other effects such as liver cancer. These data, along with results from in vitro hepatocyte studies, indicate that rodents are not good animal models for predicting the hepatic effects of phthalates in primates, including humans.

Comparative in vivo hepatic effects of Di-isononyl phthalate (DINP) and related C7-C11 dialkyl phthalates on gap junctional intercellular communication (GJIC), peroxisomal beta-oxidation (PBOX), and DNA synthesis in rat and mouse liver.

The short-term hepatic effects of DINP (CAS 68515-48-0, designated DINP-1) in rats and mice were evaluated at tumorigenic and nontumorigenic doses from previous chronic studies. Groups of male F344 rats were fed diets with DINP-1 at concentrations of 0, 1000, or 12,000 ppm and male B6C3F1 mice at 0, 500, or 6000 ppm DINP-1. After 2 or 4 weeks of treatment, changes in liver weight, gap junctional intercellular communication (GJIC), peroxisomal beta-oxidation (PBOX), and replicative DNA synthesis were examined. In addition, hepatic and serum concentrations of the parent compound and major metabolites were determined. Relative to controls in both species, increased liver weight and PBOX at the high dose of DINP-1 were consistent with peroxisomal proliferation. Hepatic GJIC was inhibited and DNA synthesis was increased at the high dose of DINP-1, which is also consistent with the tumorigenic response in rats and mice reported in other chronic studies at these doses. These hepatic effects were not observed at the low doses of DINP-1. At comparable low doses of DINP-1 in other chronic studies, no liver tumors were observed in rats and mice. The monoester metabolite (MINP-1) was detected in the liver at greater concentrations in mice than rats. This result is also consistent with the dose-response observations in rat and mouse chronic studies. Additionally, other structurally similar dialkyl phthalate esters ranging from C7 to C11 were evaluated using a similar protocol for comparison to DINP-1; these included an alternative isomeric form of DINP (DINP-A), di-isodecyl phthalate (DIDP), di-isoheptyl phthalate (DIHP), di-heptyl, nonyl undecyl phthalate (D711P), and di-n-octyl phthalate (DNOP). Collectively, these data indicate that in rats and mice, DINP-1 and other C7-C11 phthalates exhibit a threshold for inducing hepatic cellular events. Further, where previous chronic data were available for these compounds, these phthalates elicited hepatic effects at doses that correlated with the tumorigenic response. Overall, these studies suggest a good correlation between the inhibition of GJIC when compared with the data on production of liver tumors in chronic studies.

Retrospective evaluation of alpha 2u-globulin accumulation in male rat kidneys following high doses of diisononyl phthalate.

Diisononyl phthalate (DINP), a widely used plasticizer, has been evaluated in two chronic studies in rats and one in mice. In the early 1980s, Exxon found no carcinogenic potential at the estimated maximum tolerated dose (MTD) of 0.6% (307 mg/kg/ day for male rats) administered in the diet of rats for 2 years. A recent study conducted at dietary levels up to 1.2% DINP (733 mg/kg/d for male rats) reported kidney tumors in male rats at the high treatment level, but not in female rats nor mice of either sex. Because these tumors occurred only in male rats, and only at high doses, the male rat-specific alpha 2u-globulin (alpha2UG) mechanism of action was investigated. Technological advances in immunohistochemical staining and computerized image analysis techniques permitted measuring the accumulation of alpha2UG in archived kidneys from the earlier Exxon study. Using archived tissue obtained at the 12-month interim sacrifice, we identified a dose-dependent accumulation of alpha2UG in specific regions of male rat kidneys only. An increase in cell proliferation was confirmed by immunohistochemical detection of proliferating-cell nuclear antigen (PCNA) and was confined to the areas of alpha2UG accumulation. H and E-stained sections revealed tubular epithelial hypertrophy and regeneration, consistent with the immunohistopathology findings. These findings are consistent with the alpha2UG mechanism of tumorigenesis, which is not regarded as relevant for humans. Thus, exposure to DINP produced a dose-dependent alpha2UG accumulation in male rat kidneys, significant at a dietary level of 0.6% and a likely mechanism for the kidney tumors seen only in male rats administered higher dietary levels of DINP.

Evaluation of 13-week inhalation toxicity study on methyl t-butyl ether (MTBE) in Fischer 344 rats.

Methyl-t-butyl ether (MTBE) is widely used as an octane enhancing agent in gasoline. A 13-week inhalation study was conducted in Fischer 344 rats to provide information on potential target organs and toxicity of MTBE, and to ascertain a no-observed-adverse-effect level (NOAEL) for MTBE. Male and female Fischer 344 rats were exposed to target doses of MTBE vapor of 0, 800, 4000 and 8000 ppm for 6 h a day, 5 days per week for 13 weeks: MTBE produced no mortalities. At 8000 ppm, males and females showed a decrease in body weights compared to controls. The only notable effect on clinical observation was ataxia at 8000 ppm, which was apparent during the first 4 weeks of treatment. Mild hematological and clinical chemistry changes were observed in the 8000 ppm group. At 8000 ppm, animals showed increased serum levels of corticosteroids, which suggest some stress-like effect. At necropsy, there were no treatment-related gross lesions. Absolute and relative organ weights (liver, adrenals and kidneys) were increased in both sexes at 4000 and 8000 ppm, but there were no microscopic lesions in these tissues with the exception of the kidney. Microscopic examination of other tissues revealed no effects with the exception that at 8000 ppm, male rats showed: mild increased size of hyaline droplets within the kidney, mild increase in hemosiderosis in the spleen and higher incidence of hyperplasia in the lymph nodes. The highest NOAEL was judged at 800 ppm.

Chronic toxicity and carcinogenic evaluation of diisononyl phthalate in rats.

Groups of 110 Fischer 344 rats/sex were fed diisononyl phthalate (DINP) at dietary levels of 0, 0.03, 0.3, and 0.6 wt% for periods up to 2 years. Interim sacrifices of 10 predesignated rats/sex/dose were at 6, 12, and 18 months with surviving animals sacrificed at 24 months. At study termination, survival was in excess of 60% for every group. At the mid or high dose, the following biological effects were noted: slight decreases in food consumption and body weight; slight increase in mortality; a dose-related increase in relative organ weights of liver and kidney; and some slight effects on urinalysis, hematologic, and clinical chemistry parameters. No peroxisome induction was observed in livers of treated rats compared with controls. No clear treatment-related nonneoplastic or neoplastic lesions were found. However, mononuclear cell leukemia (MNCL) and changes known to be associated with an increased incidence of MNCL were seen in the mid-dose and high-dose groups. A literature review suggests that MNCL is a common finding in aging F344 rats and that this increased incidence in rats treated with DINP is not relevant to man. A clear no-observed-effect level was demonstrated for all biological end points at a dietary level of 0. 03 wt% or approximately 17 mg/kg/day of DINP.

Metabolic and peroxisome proliferation studies with di(2-ethylhexyl)phthalate in rats and monkeys.

Male Fischer 344 rats and cynomolgus monkeys were treated with various doses of di(2-ethylhexyl)phthalate (DEHP) for at least 21 days. There was metabolic, biochemical, and morphological evidence for peroxisomal proliferation in rats that consumed diets containing 1000 ppm DEHP and above. These diets were estimated to provide average daily doses of about 100 mg/kg of DEHP. In contrast, peroxisomal proliferation was not observed in monkeys that received up to 500 mg/kg/day of DEHP by gavage. The results of this study suggest that rats do not provide a good model for predicting the results of DEHP exposure on peroxisomal proliferation in higher primates.

An evaluation of the genotoxic potential of di-isononyl adipate.

Di-isononyl adipate (DINA) is one of a group of adipates used primarily as plasticizers. Concern over the mutagenic and carcinogenic potential of these materials was stimulated by the finding that one member of this class, di-(2-ethylhexyl) adipate (DEHA), induced liver tumors in female mice in a chronic feeding study. Accordingly, the genotoxic potential of DINA was evaluated in a battery of in vitro tests including the Salmonella/mammalian microsome mutagenicity assay, the mouse lymphoma TK +/-assay, and two tests of morphologic transforming ability, the BALB 3T3 and the Syrian hamster embryo in vitro transformation assays. DINA did not exhibit any evidence of mutagenic or transforming potential in any of the assays utilized.

A tissue culture model of methyl ethyl ketone's potentiation of n-hexane neurotoxicity.

Recent clinical and experimental animal studies indicate that methyl ethyl ketone (MEK), a widely used industrial solvent, can potentiate hexacarbon neurotoxicity. Organotypic tissue cultures, consisting of fetal mouse spinal cord, dorsal root ganglia, and muscle were used to reproduce this interaction. Cultures exposed to mixtures of MEK and neurotoxic doses of n-hexane developed giant axonal swellings more rapidly than those treated with equivalent doses of n-hexane alone. Cultures exposed to "no-response" doses of n-hexane in combination with MEK also developed axonal swellings. In addition, occasional cultures exposed to high levels of MEK alone and in certain combinations with n-hexane developed intra-axonal inclusions which were identified by electron microscopy to be foci of axoplasmic debris.