Di(2-ethylhexyl) adipate plasticizer triggers hepatic, brain, and cardiac injury in rats: Mitigating effect of Peganum harmala oil.

Di(2-ethylhexyl) adipate (DEHA) is a widely used plasticizer and prevalent environmental contaminant. In this study, DEHA concentrations in the milk, cheese, and butter samples wrapped with food-grade commercial polyethylene films and stored at 4 °C for 30 days were detected using gas chromatographic analysis. Also, the effects of exposure to a high dose of DEHA for a long duration on the liver, brain, and heart of Wistar rats were assessed. Besides, the possible beneficial effect of Peganum harmala oil (PGO), in relieving DEHA induced adverse effects was explored. For this purpose, four groups (8 rats/group) were orally given physiological saline, PGO (320 mg/kg bwt), DEHA (2000 mg/kg bwt), or PGO + DEHA for 60 days. The results revealed that the DEHA concentrations in the tested dairy products were ordered as follows: (butter > cheese > milk). Notably, the detected levels in butter were higher than the specific migration limit in foods. DEHA induced a significant increase in the serum levels of glucose, alanine transaminase, aspartate transaminase, acetylcholine esterase, creatine kinase-myocardium bound, malondialdehyde, tumor necrosis factor-α, and interleukin-1ß. But, significant hypoproteinemia, hypoalbuminemia, hypoglobulinemia, and hypocholesterolemia were evident following DEHA exposure. A significant reduction in the serum level of superoxide dismutase, reduced glutathione, and brain-derived neurotrophic factor was recorded. Besides, a significant downregulation in hepatic CYP2E1, brain glial fibrillary acidic protein, and cardiac troponin I gene expression was noticed. Moreover, DEHA exposure induced a significant decrease in Bcl-2 immunolabeling, but Caspase-3 immunoexpression was increased. On the contrary, PGO significantly recused DEHA injurious impacts. Therefore, PGO could represent a promising agent for preventing DEHA-induced hepatotoxicity, neurotoxicity, and cardiotoxicity.

A crosslinking strategy to make neutral polysaccharide nanofibers robust and biocompatible: With konjac glucomannan as an example.

Neutral polysaccharides such as konjac glucomannan, starch and pullulan are abundant in nature and have unique property. Their nanofibers hold great potential for biomedicine, which however, are seldom applied in the field due to the lack of crosslinking method. In this work, we report a periodate oxidation - adipic acid dihydrazide (ADH) crosslinking strategy to prepare robust and biocompatible neutral polysaccharide nanofibers. Neutral polysaccharides with adjacent dihydroxyl groups are firstly partially oxidized with periodate to give dialdehyde polysaccharides, and their electrospun nanofibers are then crosslinked with ADH to form dihydrazone crosslinkers. The resulting crosslinked neutral polysaccharide nanofibers exhibit high water resistance and excellent mechanical properties because of the high reactivity of Schiff base crosslinking reaction. Moreover, the crosslinked neutral polysaccharide nanofibers show good biocompatibility due to the low toxicity of ADH. These robust and biocompatible neutral polysaccharide nanofibers are expected to seek extensive applications in a variety of biomedical fields.

Detection and quantification analysis of chemical migrants in plastic food contact products.

Plastic food contact materials (FCM)-based products were widely used in everyday life. These products were normally imposed to strict regulations in order to pass the enforcement tests of compliance as a prefix condition. However, even in these "qualified" materials, unknown chemical substances, not involving in legislation lists, could migrate from FCM. In this perspective, the present work aims to thoroughly analyze by means of Gas Chromatography-Mass Spectrometry (GC-MS) the different substances/migrants in 120 qualified FCM plastic products. Unexpectedly, among the identified compounds (nearly 100), only 13% was included in the permitted list of Commission Regulation EU No 10/2011. All the identified compounds were classified into 11 categories according to their chemical structure and the FCM type, whereas toxicology data were in addition analyzed. Each plastic type exhibited different preferences of chemical migrants. Fortunately, most of the compounds identified were of low toxicity, and only 4 chemicals were included in priority lists and previous literature reports as potential risk factors. Subsequently, the accurate amount of these 4 chemicals was determined. The amount of Bis(2-ethylhexyl) adipate (DEHA) and Bis(2-ethylhexyl) phthalate (DEHP) were lower than the SML in Commission Regulation EU No 10/2011, and that of stearamide was under the recommended use quantity. The 2,4-di-tert-butylphenol (2,4-DTBP) was widely exist in the investigated FCM products. Among them, the highest level is obtained in polypropylene/low density polyethylene (BOPP/LDPE) materials, up to 45.568±31.513 mg/kg. In summary, a panel of unlisted chemical migrants were discovered and identified by GS-MS screening. The results implied that plastic FCMs were not so "inert" as they usually considered, and further safety evaluation should be performed toward the complete identification of new substances in FCM products.

Uncommon occupational lung diseases: high-resolution CT findings.

OBJECTIVE: The purpose of this article is to describe the high-resolution CT (HRCT) features of uncommon occupational lung diseases. CONCLUSION: HRCT plays an increasing role in the evaluation of occupational lung diseases. We present several cases of unusual occupational lung diseases and their HRCT findings. The diseases studied were siderosis, talcosis, berylliosis, calcicosis, hypersensitivity pneumonitis (due to wheat flour and isocyanates), and Ardystil syndrome. The characteristic HRCT findings together with clinical features and related occupational history improve the diagnostic accuracy of these diseases.

Collaborative work on evaluation of ovarian toxicity. 9) Effects of 2- or 4-week repeated dose studies and fertility study of di(2-ethylhexyl)adipate (DEHA) in female rats.

The present study was designed to confirm whether or not the ovarian toxicity of di(2-ethylhexyl)adipate (DEHA), which is known to have effects on female fertility, could be evaluated by the new method of histopathological examination of the ovaries in repeated dose toxicity. DEHA was orally administered to Crl:CD(SD) female rats at the doses of 0, 200, 1,000 and 2,000 mg/kg for 2 or 4 weeks in repeated dose toxicity study and for 2 weeks before mating, throughout mating and until Gestation Days 7 in female fertility. In the repeated dose toxicity studies, increase in atresia of large follicle, decrease in currently formed corpus luteum and follicular cyst were observed in the 1,000 mg/kg and above groups, suggesting that DEHA disturbed ovulation and large follicle growth. In the fertility study, a significant increase in mean estrus cycle length and post-implantation loss rate were observed in the 1,000 mg/kg and above groups, and a significant decrease in implantation rate and number of live embryos and a significant increase in pre-implantation loss rate were observed in the 2,000 mg/kg group. The histopathological changes of ovary observed in the repeated dose toxicity studies were correlated with the result that DEHA affected the estrus cycle in the female fertility study. In conclusion, a 2-week administration period is sufficient for detection of the ovarian toxicities following treatment with DEHA by new histopathological examination of the ovaries.

Dietary exposure to chemical migrants from food contact materials: a probabilistic approach.

A two-dimensional probabilistic model has been developed to estimate the short-term dietary exposure of UK consumers to migrants from food packaging materials. The current EU approach uses a default scenario of assuming that all individuals are 60 kg weight and consume 1 kg of food packaged in the material of interest per day. Using four UK National Dietary and Nutrition Surveys comprising 4-7 day dietary records for different age groups and survey years, a sample representative of the UK population has been obtained consuming around 4200 different food items. Each survey provides records for around 2000 individuals and supplies detailed information on the consumption of food and data on sex, height and socio-economic status which may be used to analyse the exposure of selected groups within the community. As a result we are able to address the variation in consumption of food amongst individuals, and account for actual body weights providing a more accurate representation of the 'true' exposure. The migrants bisphenol A diglycidyl ether (BADGE), di-2-ethylhexyl adipate (DEHA) and styrene were considered as specimen compounds although the methodology employed has the flexibility to adapt to other migrants and packaging types and indeed other food contaminants. Exposure for each individual is estimated by calculating and summing the individual exposure from each item in their diet, and is repeated for all individuals in each survey to produce a distribution of exposures for the population. The packaging type of each food item is assigned by utilizing known packaging types from the database or, by sampling from a distribution based upon market share information. The parameters contributing towards the exposure from a packaged dietary item are migrant concentration and item weight. Distributions are used to represent the inherent variation and uncertainty affecting these parameters. Where data on concentrations for a particular type of food are lacking, expert judgement is used to extrapolate from available data for other food types. The model can also be run using only migration data for food simulants. In this case, concentrations expected for each of the food items are assigned based on the data for the relevant food simulant. The primary outputs of the model are distributions of estimated daily intakes for the selected population. Each distribution gives the variation across the population subject to the uncertain parameters sampled in that iteration of the model. Analysing the ensemble of distributions allows us to obtain the confidence limits around estimates for percentiles due to the uncertainties. The probabilistic approach allows sensitivity analysis to evaluate the relative importance of the input parameters and places confidence bounds on the outputs to show the effect of the uncertainties and the contribution of each food type toward the overall exposure.

Induction of heat shock protein 70 in rat olfactory epithelium by toxic chemicals: in vitro and in vivo studies.

We have previously developed a rat nasal explant system for investigating upper respiratory tract toxicity, and the aims of this study were to determine whether heat shock protein (HSP) 70 is induced in this model following exposure to carbon tetrachloride (CCl4), dimethyl adipate (DMA), methyl iodide (CH3I) or paracetamol, and whether HSP70 can also be induced in the nasal cavity in vivo. Intracellular ATP was significantly depleted in ethmoturbinates incubated for 4 h with the toxins (0-100 mM; EC50 concentrations: CCl4 32 mM, DMA 3 mM, CH3I 1.5 mM, paracetamol 70 mM), but there was little induction of HSP70. Turbinates were then incubated for 1 h with CCl4 (5 mM), DMA (1.5 mM), CH3I (0.57 mM) or paracetamol (30 mM) and allowed to recover for up to 24 h. Treatment with CCl4, DMA or paracetamol resulted in 250-300% induction of HSP70. Male rats were administered a single oral dose of CCl4 (1600 mg/kg) and killed 16 h later. Degenerative lesions (epithelial undulation and hydropic vacuolation) were evident in the olfactory epithelium, and immunohistochemical analysis of HSP70 revealed increased staining in, or proximate to, areas of damage. Thus, HSP70 can be induced in the olfactory epithelium both in vitro and in vivo.

Occurrence of twenty-six endocrine-disrupting compounds in environmental water samples from Catalonia, Spain.

We monitored 26 compounds known or suspected to be endocrine disruptors in several environmental water samples from a river, the sea, and an irrigation canal. Because of the various chemical properties of the compounds monitored, analyses were carried out by using two different methods. One method is based on solid-phase extraction (SPE) on-line coupled to gas chromatography-mass spectrometry through an on-column interface. Another is based on high-performance liquid chromatography-(electrospray) mass spectrometry working in negative ionization mode and using off-line SPE. The limits of detection for the two methods were at levels of low microg/L. Phthalates and bis-(2-ethylhexyl) adipate were found at levels between 0.05 and 13 microg/L in all of the water samples analyzed. Some pesticides, alkylphenols, and estrogens were determined in a few samples at levels below 0.1 microg/L.

Final report on the safety assessment of Stearamide DIBA-Stearate.

Stearamide DIBA-Stearate is a substituted dihydroxyisobutylamine (DIBA) that functions in cosmetic formulations as an opacifying agent, a surfactant-foam booster, and a viscosity increasing agent. Stearamide DIBA-Stearate was reportedly used in four cosmetic formulations, at concentrations of 1% to 3%. Few data on this ingredient were available. Data on related ingredients, including Dibutyl Adipate, Diisopropyl Adipate, Stearamide DEA, and Stearamide MEA, were considered in the assessment of safety. A formulation containing 1.3% Stearamide DIBA-Stearate (further diluted to 4% of the formulation) was mildly irritating but nonsensitizing in an repeated-insult patch test (RIPT). The same dilution was noncomedogenic. At a concentration of 20%, Dibutyl Adipate had an oral LD50 of 2 g/kg. Subchronic dermal exposure of rabbits (1.0 ml/kg/day) caused a reduction in weight gain that was not observed at a dose of 0.5 ml/kg/day. In studies using rabbits, undiluted Dibutyl Adipate caused mild to moderate skin irritation and minimal ocular irritation. When pregnant rats were treated intraperitoneally with approximately 1.75 ml/kg Dibutyl Adipate during gestation, the incidence of fetal gross abnormalities was increased. No effect was observed at smaller doses. Diisopropyl Adipate had low acute oral and percutaneous toxicity, and was only a very mild ocular irritant. In skin irritation studies using rabbits, 5.0% to 100% Diisopropyl Adipate caused minimal to mild irritation; these results were also seen in clinical testing with only moderate cumulative irritation, and no sensitization or photosensitization. A formulation containing 5.27% Stearamide MEA was not toxic to rats when applied topically daily for 13 weeks. In studies using rabbits, Stearamide DEA (35% to 40%) was not a skin or ocular irritant, and Stearamide MEA (5.27%) was not an ocular irritant. At 17%, Stearamide MEA was not irritating to the skin, but caused minimal to moderate irritation to the eyes of rabbits. Stearamide MEA (5.27%) did not cause sensitization during a clinical study. It was not possible, however, to determine the relevance of these data on related ingredients. Therefore, it was concluded that the available data are insufficient. Additional data needs are (1) method of manufacture; (2) chemical characterization, including impurities; (3) dermal absorption; if significantly absorbed, then a 28-day dermal toxicity study and a reproductive and developmental toxicity study may be needed; (4) two genotoxicity assays, at least one in a mammalian system; if positive, then a 2-year dermal carcinogenesis study using National Toxicology Program (NTP) methods may be needed; (5) ultraviolet (UV) absorption data; if significant absorption occurs in the UVA or UVB range, photosensitization data are needed. Absent these data, it was concluded that the available data are insufficient to support the safety of Stearamide DIBA-Stearate as used in cosmetic products.

Comparison of the effects of di-(2-ethylhexyl)adipate on hepatic peroxisome proliferation and cell replication in the rat and mouse.

The effects of di-(2-ethylhexyl)adipate (DEHA) have been compared in female F344 rats and female B6C3F1 mice fed diets containing 0-4.0% DEHA and 0-2.5% DEHA, respectively, for periods of 1, 4 and 13 weeks. In both the rat and mouse treatment with DEHA at all time points produced a dose-dependent increase in relative liver weight and hepatic peroxisome proliferation as demonstrated by the induction of peroxisomal (cyanide-insensitive palmitoyl-CoA oxidation) and microsomal (lauric acid 12-hydroxylase) fatty acid oxidising enzyme activities. The magnitude of induction of peroxisome proliferation was similar in both species. Replicative DNA synthesis was studied by implanting osmotic pumps containing 5-bromo-2'-deoxyuridine during study weeks 0-1, 3-4 and 12-13. After 1 week DEHA treatment hepatocyte labelling index values were increased in rats given 2.5 and 4.0% DEHA and mice given 0.6-2.5% DEHA. While DEHA treatment for 4 and 13 weeks did not increase labelling index values in the rat, a sustained stimulation of replicative DNA synthesis was observed in mice given 1.2 and 2.5% DEHA. The results of this study demonstrate a species difference in the hepatic effects of DEHA, in that at some dose levels DEHA can produce a sustained stimulation of replicative DNA synthesis in mouse but not in rat liver. Sustained cell replication provides a better correlation with the observed formation of liver tumours in chronic studies with DEHA in female mice, but not in female rats, than the magnitude of stimulation of hepatic peroxisome proliferation.

Mixture risk assessment: a case study of Monsanto experiences.

Monsanto employs several pragmatic approaches for evaluating the toxicity of mixtures. These approaches are similar to those recommended by many national and international agencies. When conducting hazard and risk assessments, priority is always given to using data collected directly on the mixture of concern. To provide an example of the first tier of evaluation, actual data on acute respiratory irritation studies on mixtures were evaluated to determine whether the principle of additivity was applicable to the mixture evaluated. If actual data on the mixture are unavailable, extrapolation across similar mixtures is considered. Because many formulations are quite similar in composition, the toxicity data from one mixture can be extended to a closely related mixture in a scientifically justifiable manner. An example of a family of products where such extrapolations have been made is presented to exemplify this second approach. Lastly, if data on similar mixtures are unavailable, data on component fractions are used to predict the toxicity of the mixture. In this third approach, process knowledge and scientific judgement are used to determine how the known toxicological properties of the individual fractions affect toxicity of the mixture. Three examples of plant effluents where toxicological data on fractions were used to predict the toxicity of the mixture are discussed. The results of the analysis are used to discuss the predictive value of each of the above mentioned toxicological approaches for evaluating chemical mixtures.

Peroxisome proliferation due to di (2-ethylhexyl) adipate, 2-ethylhexanol and 2-ethylhexanoic acid.

The dose-response relationships for peroxisome proliferation due to Di (2-ethylhexyl) adipate (DEHA), 2-ethylhexanol (EH), 2-ethylhexanoic acid (EHA) have been investigated in rats and mice. Linear dose-response relationships were observed for induction of cyanide-insensitive palmitoyl CoA oxidation (PCO), used as a enzyme marker of peroxisome proliferation, by DEHA, EH and EHA in both species. Relative liver weights were also increased in a dose related manner. On a molar basis, DEHA was twice as potent as EH or EHA which were equipotent and PCO was stimulated to a greater extent in male mice than in rats or female mice. At doses above 8 mmol/kg/day, EH was toxic to rats (both sexes) and similarly EHA at 13.5 mmol/kg/day lead to the death of female rats. In a attempt to explain the species difference in carcinogenicity of DEHA previously reported, we also used Fischer 344 rats and B6C3F1 mice. DEHA administration (2.5 g/kg/day) to Fischer 344 rats and B6C3F1 mice lead to toxicity in female rats. Relative liver weights were increased in a dose related fashion by DEHA administration to both rats and mice, PCO but not catalase was markedly increased (up to 15 fold in male rats). Light microscopy examination indicated some glycogen loss, a dose related hypertrophy and increased eosinophilia in both rats and mice. Electron microscopy confirmed peroxisome proliferation accompanied by a marked reduction of lipid in the centrilobular hepatocytes. These data suggest EHA to be the proximate peroxisome proliferator derived from DEHA.(ABSTRACT TRUNCATED AT 250 WORDS)

Non-mutagenicity of 4 metabolites of di(2-ethylhexyl)phthalate (DEHP) and 3 structurally related derivatives of di(2-ethylhexyl)adipate (DEHA) in the Salmonella mutagenicity assay.

Four metabolites of the rat liver carcinogen di(2-ethylhexyl)phthalate (DEHP) (mono-(2-ethylhexyl)phthalate, mono-(2-ethyl-5-hydroxyhexyl)phthalate, mono-(2-ethyl-5-oxohexyl)phthalate, and mono-(5-carboxy-2-ethylpentyl)phthalate) and 3 structurally related derivatives of di(2-ethylhexyl)adipate (DEHA) (mono-(2-ethylhexyl)adipate, mono-(2-ethyl-5-hydroxyhexyl)adipate, and mono-(2-ethyl-5-oxohexyl)adipate) were tested for mutagenicity in the Ames assay using Salmonella typhimurium strains TA97, TA98, TA100, and TA102, with and without a metabolic activation preparation. Aroclor 1254-induced rat liver S9 and DEHP-induced rat liver S9 were used. Concentrations of these compounds up to 1000 micrograms/plate were negative with all tester strains in the presence or absence of metabolic activation.

In vitro steady-state levels of hydrogen peroxide after exposure of male F344 rats and female B6C3F1 mice to hepatic peroxisome proliferators.

The hypothesis that hepatocarcinogenesis resulting from treatment of rats and mice with peroxisome proliferators is linked to increased cellular levels of hydrogen peroxide from peroxisomal beta-oxidation was investigated. Male F344 rats and female B6C3F1 mice were treated for 14 days with di(2-ethylhexyl)phthalate (DEHP) or di(2-ethylhexyl)adipate (DEHA), industrial plasticizers, or nafenopin, a hypolipidemic drug. Activities of enzymes responsible for the production [peroxisomal palmitoyl CoA oxidase (PCO)] and degradation [catalase (Cat) and glutathione peroxidase (GSHPx)] of H2O2 were assayed in liver homogenates prepared from treated animals. The activities of the peroxisomal enzymes PCO and Cat were enhanced 5- to 25-fold and 1.5- to 3-fold respectively by treatment with the peroxisome proliferators. The activity of GSHPx, a cytoplasmic enzyme, was decreased 40-60% in liver homogenates prepared from treated animals compared to control animals. A kinetic treatment of the rates of formation of hydrogen peroxide by PCO, and of degradation of hydrogen peroxide by catalase was used to estimate steady-state hydrogen peroxide concentrations ([H2O2]) during peroxisomal oxidation of palmitoyl CoA. Increases in peroxisomal steady-state [H2O2] for the F344 rat liver homogenates correlated well with the carcinogenic potential of these chemicals, determined in previous carcinogenicity studies. Increases in the steady-state [H2O2] were also calculated for liver homogenates prepared from mice treated with these compounds. Decreases in liver lipid peroxidation were observed after treatment with each chemical in both species. The results of these studies are consistent with an involvement of increased peroxisomal hydrogen peroxide in the hepatocarcinogenesis of these compounds.

Carcinogenic potential of phthalic acid esters and related compounds: structure-activity relationships.

Chronic toxicity and carcinogenicity studies of several phthalic acid esters (PAEs) and compounds containing a 2-ethylhexyl moiety were conducted in Fischer 344 rats and B6C3F1 (hybrid) mice. The compounds studied were phthalic anhydride, di(2-ethylhexyl) phthalate, butyl benzyl phthalate, diallyl phthalate, di(2-ethylhexyl) adipate, tris(2-ethylhexyl) phosphate, and 2-ethylhexyl sulfate (sodium salt). Estimated maximum tolerable doses and fractionally lower doses of each compound were administered to groups of 50 male and 50 female rats and mice for 2 years, followed by sacrifice, necropsy, and histopathological examination of major organs and tissues. The low toxic potencies of most of the compounds allowed for relatively high doses to be given during the chronic studies. In general, the toxic manifestations of the PAEs were closely correlated with their ester substituents. Although many of the PAEs possessed some carcinogenic activity, target sites for such effects were dissimilar, suggesting the absence of a common mode of action. In contrast, all of the 2-ethylhexyl-containing compounds studied possessed some hepatocarcinogenic activity, indicating that this moiety may have a propensity for causing hepatocarcinogenesis in mice, particularly those of the female sex. The 2-ethylhexyl compound that caused the greatest hepatocarcinogenic response in mice, di(2-ethylhexyl) phthalate, was also hepatocarcinogenic in rats. Similarly, those with a relatively greater effect in female mice were also active in male mice. Thus, sex and species differences in 2-ethylhexyl-induced hepatocarcinogenesis in rodents are probably quantitative rather than qualitative in nature.

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.

Comparative chronic toxicities and carcinogenic potentials of 2-ethylhexyl-containing compounds in rats and mice.

Four compounds containing a 2-ethylhexyl moiety [di(2-ethylhexyl)phthalate (DEHP), di(2-ethylhexyl)adipate (DEHA), tris(2-ethylhexyl)phosphate (TEHP), and 2-ethylhexyl sulfate (EHS)] were tested for carcinogenic and other chronic and subchronic toxic effects in 90-day and 2-year studies in male and female Fischer 344 rats and B6C3F1 mice. The low generalized toxic potencies of the test chemicals allowed relatively high doses of all of these compounds to be administered. Despite differences in chemical structure, all four chemicals were related to increased occurrences of hepatocellular neoplasms, principally carcinomas, in female mice. DEHA and DEHP also induced hepatocellular neoplasms in male mice, while DEHP caused hepatocellular neoplasms in both male and female rats. No other neoplasms were considered to be unequivocally related to compound administration in these studies. There was a positive correlation between the magnitude of the hepatocarcinogenic response in female mice and the probability of a hepatocarcinogenic response in male mice and in male and female rats, suggesting quantitative differences in the carcinogenic potentials of these agents. These results suggest that compounds containing a 2-ethylhexyl moiety (and 2-ethylhexanol, by implication) may possess some carcinogenic potential, especially for the rodent liver. No other organ-specific toxic effects common to two or more test chemicals were observed in these studies.

Genotoxicity studies on di-(2-ethylhexyl) phthalate and adipate and toxicity studies on di-(2-ethylhexyl) phthalate in the rat and marmoset.

These studies have provided evidence that DEHP and DEHA do not bind covalently to DNA and do not therefore possess the characteristics of a genotoxic agent (Lutz, 1982). This suggests that the tumours induced in the rodent liver may result from some non-genotoxic mechanism and supports the view that the weakly positive dominant lethal test seen on administration of DEHP by the ip (but not the oral) route (Singh et al. 1974) is unlikely to have resulted from a direct effect on the genome of the sperm cells. Although the mechanism responsible for the induction of tumours by high doses of DEHP in rodents is not clear, it would appear both from these studies and from work on hypolipidaemic agents, that peroxisomal proliferation and the induction of enzymes associated with this organelle are in some way implicated (Cohen & Grasso, 1981). Other studies have shown that changes of this type are produced by doses of hypolipidaemic agents that induce liver cancer in rodents (Cohen & Grasso, 1981) and our investigations have indicated that they were also prominent at dose levels of DEHP similar to those that induced liver cancer in the NCI study (National Toxicology Program, 1982). No cancer induction would be expected to occur in the absence of these changes. In our dose-response study in rats it was shown that at the lowest dose (50 mg/kg body weight/day, approximately equivalent to a dietary level of 1000 ppm) several effects seen with higher doses were not apparent and others differed only slightly from normal control values. This is particularly relevant to assessments of the risk posed by DEHP and DEHA present as contaminants in foods, since human exposure via the food chain has been estimated by Shiota, Chou & Nishimura (1980) as 30 micrograms/kg body weight/day, several orders of magnitude less than the lowest exposure level used in these experiments. In addition, our studies indicate that none of the changes found in the rat were observed in the marmoset, suggesting that rodents and primates differ fundamentally in their hepatic and testicular response to DEHP. Previous studies by other authors (reviewed by Cohen & Grasso, 1981) indicated that morphological changes in the endoplasmic reticulum and the proliferation of peroxisomes are not features of the response of monkeys and man to high doses of hypolipidaemic agents.(ABSTRACT TRUNCATED AT 400 WORDS)