Lack of induction of hepatic DNA damage on long-term administration of peroxisome proliferators in male F-344 rats

In order to evaluate the relationship between hydrogen peroxide (H2O2) generation and subsequent DNA damage caused by peroxisome proliferation, we examined DNA damage and changes in peroxisomal beta-oxidation activity in rat liver. Male F-344 rats were given orally clofibrate, bezafibrate or di(2-ethylhexyl)phthalate (DEHP) for up to 78 weeks. In rats fed DEHP for 52 or 78 weeks hepatocarcinomas or neoplastic nodules were found. In rats treated for 2 weeks with peroxisome proliferators, peroxisomal beta-oxidation activity was increased 10-17 times over control levels. After long-term treatment (20-78 weeks), the level of peroxisomal beta-oxidation activity remained 3-13-times higher in each group. When single strand DNA breaks were measured by a DNA-alkaline elution technique, no increase in DNA damage was observed in livers from rats fed peroxisome proliferators for 2, 40 or 78 weeks. In rats bearing hepatocarcinomas induced by DEHP, the hepatic DNA showed significant breaks; the rate of DNA-alkaline elution was found to increase approximately 5-fold. No significant increase in hepatic lipid peroxide level was observed in each group. These results show that although prolonged treatment with peroxisome proliferators induces markedly peroxisomal beta-oxidation activity, the active oxygen species from peroxisomal beta-oxidation are not enough to give rise to significant DNA damage. Moreover, the change in the activity of peroxisomal beta-oxidation may not relate to hepatocarcinogenesis induced by peroxisome proliferators.     

Role of PPARalpha in mediating the effects of phthalates and metabolites in the liver

Phthalate esters belong to a large class of compounds known as peroxisome proliferators (PP). PP include chemicals that activate different subtypes of the peroxisome proliferator-activated receptor (PPAR) family. The ability of phthalate esters and their metabolites to activate responses through different PPAR subtypes is not fully characterized. We investigated the ability of two phthalate esters di-(2-ethylhexyl) phthalate (DEHP) and di-n-butyl phthalate (DBP) and selected metabolites to activate PPAR (alpha, beta/delta, gamma) using a transient transfection assay. The monoester of DEHP, mono-(2-ethylhexyl) phthalate (MEHP) activated all three subtypes of PPAR, but preferentially activated PPARalpha. A second metabolite of DEHP, 2-ethylhexanoic acid (2-EHXA) was a weaker activator of all three subtypes. DBP, but not the primary metabolite mono-n-butyl phthalate weakly activated all three PPAR subtypes. MEHP and DBP but not DEHP and MBP interacted directly with human PPARalpha and PPARgamma as determined by scintillation proximity assays. Both DEHP and DBP activated expression of PP-inducible gene products in wild-type but not PPARalpha-null mice suggesting that both of these phthalates exert their effects by activation of PPARalpha in vivo. The preferential activation of PPARalpha by phthalate ester metabolites suggests that these phthalates mediate their toxic effects in rodent liver in a manner indistinguishable from other PP.     

Identification of the proximate peroxisome proliferator(s) derived from di(2-ethylhexyl) phthalate

A primary rat hepatocyte culture system was utilized to determine the proximate peroxisome proliferator(s) derived from di(2-ethylhexyl) phthalate (DEHP). DEHP was administered to rats and the urinary metabolites were identified and isolated. The major metabolites were those resulting from initial omega- or omega - 1-carbon oxidation of the mono(2-ethylhexyl) phthalate (MEHP) moiety. These metabolites, together with MEHP and 2-ethylhexanol, were added to primary rat hepatocyte cultures and the effect on peroxisomal enzyme activity was determined. The omega-carbon oxidation products [mono(3-carboxy-2-ethylpropyl) phthalate (I) and mono(5-carboxy-2-ethylpentyl) phthalate (V)] and 2-ethylhexanol produced little or no effect on CN- -insensitive palmitoyl-CoA oxidation (a peroxisomal marker). MEHP and the omega - 1-carbon oxidation products [mono-(2-ethyl-5-oxohexyl) phthalate (VI) and mono(2-ethyl-5-hydroxyhexyl) phthalate (IX)] produced a large (7- to 11-fold) induction of peroxisomal enzyme activity. Similar structure-activity relationships were observed for the induction of cytochrome P-450-mediated lauric acid hydroxylase and increase in cellular coenzyme A content. This identification of the proximate proliferators will aid in the elucidation of the mechanism by which DEHP causes proliferation of peroxisomes in the rodent liver. Oral administration of MEHP (150 or 250 mg/kg) to male guinea pigs did not produce hepatic peroxisome proliferation. Addition of MEHP (0 to 0.5 mM) or one of the "active" proliferators in the rat (metabolite IX, 0 to 0.5 mM) to primary guinea pig hepatocyte cultures also failed to produce an induction of peroxisomal beta-oxidation. Possible reasons for this species difference are discussed.     

Dermal toxicity elicited by phthalates: Evaluation of skin absorption,immunohistology, and functional proteomics

The toxicity of phthalates is an important concern in the fields of environmental health and toxicology. Dermal exposure via skin care products, soil, and dust is a main route for phthalate delivery. We had explored the effect of topically-applied phthalates on skin absorption and toxicity. Immunohistology, functional proteomics, and Western blotting were employed as methodologies for validating phthalate toxicity. Among 5 phthalates tested, di(2-ethylhexyl)phthalate (DEHP) showed the highest skin reservoir. Only diethyl phthalate (DEP) and dibutyl phthalate (DBP) could penetrate across skin. Strat-M^® membrane could be used as permeation barrier for predicting phthalate penetration through skin. The accumulation of DEHP in hair follicles was ∼15 nmol/cm², which was significantly greater than DBP and DEP. DBP induced apoptosis of keratinocytes and fibroblasts via caspase-3 activation. This result was confirmed by downregulation of 14-3-3 and immunohistology of TUNEL. On the other hand, the HSP60 overexpression and immunostaining of COX-2 suggested inflammatory response induced by DEP and DEHP. The proteomic profiling verified the role of calcium homeostasis on skin inflammation. Some proteins investigated in this study can be sensitive biomarkers for dermal toxicity of phthalates. These included HSPs, 14-3-3, and cytokeratin. This work provided novel platforms for examining phthalate toxicity on skin.     

Phthalates rapidly increase production of reactive oxygen species in vivo: role of Kupffer cells

The role of oxidants in the mechanism of tumor promotion by peroxisome proliferators remains controversial. The idea that induction of acyl-coenzyme A oxidase leads to increased production of H(2)O(2), which damages DNA, seems unlikely; still, free radicals might be important in signaling in specialized cell types such as Kupffer cells, which produce mitogens. Because hard evidence for increased oxidant production in vivo after treatment with peroxisome proliferators is lacking, the spin-trapping technique and electron spin resonance spectroscopy were used. Rats were given di(2-ethylhexyl) phthalate (DEHP) acutely. The spin trapping agent alpha-(4-pyridyl-1-oxide)-N-tert-butylnitrone was also given and bile samples were collected for 4 h. Under these conditions, the intensity of the six-line radical adduct signal increased to a maximum value of 2.5-fold 2 h after administration of DEHP, before peroxisomal oxidases were induced. Furthermore, DEHP given with [(13)C(2)]dimethyl sulfoxide produced a 12-line electron spin resonance spectrum, providing evidence that DEHP stimulates (*)OH radical formation in vivo. Furthermore, when rats were pretreated with dietary glycine, which inactivates Kupffer cells, DEHP did not increase radical signals. Moreover, similar treatments were performed in knockout mice deficient in NADPH oxidase (p47(phox) subunit). Importantly, DEHP increased oxidant production in wild-type but not in NADPH oxidase-deficient mice. These data provide evidence for the hypothesis that the molecular source of free radicals induced by peroxisome proliferators is NADPH oxidase in Kupffer cells. On the contrary, radical adduct formation was not affected in peroxisome proliferator-activated receptor alpha knockout mice. These observations represent the first direct, in vivo evidence that phthalates increase free radicals in liver before peroxisomal oxidases are induced.     

Hepatic peroxisome (microbody) proliferation in rats fed plasticizers and related compounds

Male rats were fed the plasticizers di-(2-ethylhexyl) phthalate (DEHP), di-(2-ethylhexyl) adipate (DEHA), di-(2-ethylhexyl) sebacate (DEHS), adipic acid, and diethyl phthalate at a dietary concentration of 2% for 3 weeks. Hepatic peroxisome proliferation in association with an increase in liver size, increase of hepatic activities of the peroxisome-associated enzymes catalase and carnitine acetyltransferase, and hypolipidemia were observed in animals treated with DEHP, DEHA, and DEHS but not in animals fed adipic acid and diethyl phthalate. To relate structure to biological activity, additional groups of rats were fed 2-ethylhexyl alcohol (a metabolite of DEHP), hexyl alcohol. 2-ethylhexanoic acid, hexanoic acid, 2-ethylhexyl aldehyde, hexylaldehyde, and 2-ethylhexyl amine at a 2% dose level. The changes induced by 2-ethylhexyl alcohol and 2-ethylhexanoic acid were comparable to those induced by DEHP, DEHA, and DEHS, suggesting that 2-ethylhexyl alcohol is the active part of the molecule responsible for peroxisome proliferation. 2-Ethylhexyl aldehyde induced a moderate increase in peroxisome population. No effect on hepatic peroxisomes or their associated enzymes was induced by the straight-chained analogs hexyl alcohol, hexanoic acid, and hexyl aldehyde. The hepatic effects of plasticizers capable of inducing peroxisome proliferation are similar to those resulting from treatment with clofibrate and other hypolipidemic drugs.     

Comparison of oxidative stress and changes of xenobiotic metabolizing enzymes induced by phthalates in rats.

Phthalates are widely used as a plasticizer and cause a peroxisome proliferation. Peroxisome proliferators (PPs), such as di-2-ethylhexyl phthalate (DEHP) and clofibrate (CF) are known to have a hepatocarcinogenic potential in rodents. It has been proposed that these PPs may cause hepatocellular cancer by an oxidative damage-mediated mechanism(s). The primary purpose of this study is to find whether there is a difference between the oxidative damage by hepatocarcinogenic PPs (DEHP and CF) and the oxidative damage by weak PPs [di-n-butyl phthalate (DBP) and n-butylbenzyl phthalate (BBP)]. The second purpose is to investigate if phthalates can affect the phase I/phase II enzymes, and if the effect of PPs on metabolizing enzymes correlates with peroxisome proliferation or not. After rats were treated with PPs (DEHP, DBP and BBP; 50, 200, 1000 mg/kg, CF; 100 mg/kg, p.o., for 14 days), the activities of metabolizing enzymes and peroxisomal enzymes were investigated, and the oxidative damage was measured using 8-hydroxydeoxyguanosine (8-OHdG) in the DNA and malonedialdehyde (MDA) in the livers. These four PPs significantly increased the relative liver weights, palmitoyl-CoA oxidation and activity of carnitine acetyltransferase. DEHP was found to be the most potent PP among three phthalates. A dramatic and dose-dependent increase in hepatic MDA levels was observed in CF (100 mg/kg), DEHP (>or=50 mg/kg), DBP and BBP (>or=200 mg/kg) groups. However, the 8-OHdG in hepatic DNA was increased only in DEHP (1000 mg/kg) and CF groups. Activities of cytochrome p4501A1, 1A2, 3A4, UDP-glucuronosyl transferase and glutathione S-transferase were decreased overall by PPs, but there is no correlation between the inhibitory effect on metabolizing enzymes and the peroxisome proliferation. These results indicate that 8-OHdG positively correlates with carcinogenic potential of PPs, but other factors as well as peroxisomal H(2)O(2) could be involved in the generation of 8-OHdG and the carcinogenesis of PPs. The present findings also demonstrate that the effect of PPs on xenobiotic metabolizing enzymes may be independent of the peroxisome proliferation and the oxidative stress. Thus it is possible that the PPs affect the hepatic toxification/detoxification capacity even in humans.     

灌装温度对中药代煎包材中塑化剂迁移率的影响规律

目的研究中药代煎包材中邻苯二甲酸酯类塑化剂的迁移量随灌装温度的变化规律,为规范中药代煎流程提供一定的参考。方法检测中药代煎包材中17种常见邻苯二甲酸酯类塑化剂的含量;将蒸馏水煮沸后,在梯度温度下灌装到中药代煎包材中,采用气质联用色谱技术,定性定量各邻苯二甲酸酯类塑化剂的迁移率。结果GC-MS符合检测邻苯二甲酸酯类塑化剂的要求,标准曲线和相关系数显示,在0.05~5.00 mg/L呈良好线性关系,相关系数>0.998,检出限为0.002 mg/L。中药代煎包材检出的邻苯二甲酸酯类塑化剂及其含量为DEHP(0.122 mg/kg)、DBP(0.273 mg/kg)、DIBP(0.073 mg/kg)、DEP(0.024 mg/kg)和DMP(0.037 mg/kg),其他12种PAEs未检出。30~100℃的梯度温度灌装后,蒸馏水中检出的塑化剂及其迁移率分别为DEHP(0.14%~10.58%)、DBP(6.29%~20.76%)、DEP(ND^1.09%),其余未检出。结论GC-MS能够准确、快捷地检测中药代煎包材中邻苯二甲酸酯类塑化剂的含量;样品包材中PAEs及其迁移量符合GB96852016中相关要求;灌装温度与中药代煎包材中DEHP、DBP的迁移率呈正相关,灌装温度越高,DEHP、DBP的迁移率也越高;灌装温度对中药代煎包材中DIBP、DMP和DEP的迁移率没有显著影响。从减少塑化剂的迁移量和保证中药代煎效率的角度出发,中药代煎的灌装温度控制在60℃以下能显著降低DEHP、DBP的迁移量。     

Toxicity of seven phthalate esters to embryonic development of the abalone Haliotis diversicolor supertexta

The toxicity of seven phthalate esters (PAEs), dimethyl phthalate (DMP), diethyl phthalate (DEP), dibutyl phthalate (DBP), butylbenzyl phthalate (BBP), di-n-hexyl phthalate (DnHP), di-(2-ethylhexyl) phthalate (DEHP) and di-n-octyl phthalate (DOP) to embryogenesis and larval development of the marine univalve Haliotis diversicolor supertexta was examined by means of two-stage embryo toxicity test. At the blastula stage, the normal embryonic development of H. diversicolor supertexta showed a good dose-response decrease when exposed to DMP, DEP, DBP, BBP, and DnHP. 9-h EC₅₀ values of DMP, DEP, DBP, BBP, and DnHP were 55.71, 39.13, 8.37, 2.65, and 3.32 mg/l, respectively. 9-h EC₅₀ values of DEHP and DOP were not available due to their low solubility. The toxicity order of seven tested PAEs was BBP>DnHP>DBP>DEP>DMP>DOP>DEHP. With the completion of metamorphosis as an experimental endpoint, the 96-h no-observed effect concentration values of DBP, DEHP and the other five tested PAEs were 0.022, 0.021, and 0.020 mg/l, respectively. Due to simple obtainment, convenient stimulation to spawn in the lab, greater sensitivity than mature species, and short culture time, the embryos of H. diversicolor supertexta have the potential to be utilized in acute toxicity test for at least PAEs.     

Estimated exposure to phthalates in cosmetics and risk assessment

Some phthalates such as di(2-ethylhexyl) phthalate (DEHP) and dibutyl phthalate (DBP) and their metabolites are suspected of producing teratogenic or endocrine-disrupting effects. To predict possible human exposure to phthalates in cosmetics, the levels of DEHP, diethyl phthalate (DEP), DBP, and butylbenzyl phthalate (BBP) were determined by high-performance liquid chromatography (HPLC) in 102 branded hair sprays, perfumes, deodorants, and nail polishes. DBP was detected in 19 of the 21 nail polishes and in 11 of the 42 perfumes, and DEP was detected in 24 of the 42 perfumes and 2 of the 8 deodorants. Median exposure levels to phthalates in cosmetics by dermal absorption were estimated to be 0.0006 g/kg body weight (bw)/d for DEHP, 0.6 g/kg bw/d for DEP, and 0.103 g/kg bw/d for DBP. Furthermore, if phthalates in cosmetics were assumed to be absorbed exclusively via 100% inhalation, the median daily exposure levels to phthalates in cosmetics were estimated to be 0.026 g/kg bw/d for DEHP, 81.471 g/kg bw/d for DEP, and 22.917 g/kg bw/d for DBP, which are far lower than the regulation levels set buy the Scientific Committee on Toxicity, Ecotoxicity, and the Environment (CSTEE) (37 g/kg bw/d, DEHP), Agency for Toxic Substances and Disease Registry (ATSDR) (7000 g/kg bw/d, DEP), and International Programme on Chemical Safety (IPCS) (66 g/kg bw/d, DBP), respectively. Based on these data, hazard indices (HI, daily exposure level/regulation level) were calculated to be 0.0007 for DEHP, 0.012 for DEP, and 0.347 for DBP. These data suggest that estimated exposure to-phthalates in the cosmetics mentioned are relatively small. However, total exposure levels from several sources may be greater and require further investigation.     

Long-term effects of peroxisome proliferators on the balance between hydrogen peroxide-generating and scavenging capacities in the liver of Fischer-344 rats

In order to clarify whether peroxisomal hydrogen peroxide (H2O2) plays an important role in peroxisome proliferator-induced hepatocarcinogenesis, we examined the change in metabolism of peroxisomal H2O2 in vivo and in vitro using male Fischer-344 rats fed clofibrate, bezafibrate and di(2-ethylhexyl)phthalate (DEHP) for up to 78 weeks. Hepatic peroxisomal fatty acyl-CoA oxidase activity increased 12-20-fold after 2 or 4 weeks treatment; later this level gradually decreased toward controls, and at 78 weeks activity was 3-10-times of control. Although hepatic H2O2 levels were increased slightly by clofibrate, bezafibrate and DEHP, the changes did not correlate with the changes in peroxisomal fatty acyl-CoA oxidase activity. In isolated hepatocytes, the rate of leakage of peroxisomal H2O2 from peroxisomes into the cytosol and the hepatocellular H2O2 content was measured. The rate of leakage of peroxisomal H2O2 into cytosol increased 2.5-4-fold when peroxisomal beta-oxidation activity was induced by peroxisome proliferators, and the increases in this rate corresponded with changes in the peroxisomal beta-oxidation activity. In contrast, the hepatocellular H2O2 contents were not affected by induced peroxisomal beta-oxidation. These data show that H2O2 leaking from peroxisome into cytosol would be quickly decomposed, and thus peroxisomal H2O2 does not appear to play an important role in hepatocarcinogenesis by such an oxidative stress mechanism after the long-term treatment with peroxisome proliferators.     

Biological impact of phthalates

Esters of phthalic acid are chemical agents used to improve the plasticity of industrial polymers. Their ubiquitous use in multiple commercial products results in extensive exposure to humans and the environment. This study investigated cytotoxicity, endocrine disruption, effects mediated via AhR, lipid peroxidation and effects on expression of enzymes of xenobiotic metabolism caused by di-(2-ethy hexyl) phthalate (DEHP), diethyl phthalate (DEP), dibutyl phthalate (DBP) and benzyl butyl phthalate (BBP) in developing fish embryos. Oxidative stress was identified as the critical mechanism of toxicity (CMTA) in the case of DEHP and DEP, while the efficient removal of DBP and BBP by phase 1 enzymes resulted in lesser toxicity. DEHP and DEP did not mimic estradiol (E₂) in transactivation studies, but at concentrations of 10 mg/L synthesis of sex steroid hormones was affected. Exposure to 10 mg BBP/L resulted in weak transactivation of the estrogen receptor (ER). All phthalates exhibited weak potency as agonists of the aryl hydrocarbon receptor (AhR). The order of potency of the 4 phthalates studied was; DEHP > DEP > BBP >> DBP. The study highlights the need for simultaneous assessment of: (1) multiple cellular targets affected by phthalates and (2) phthalate mixtures to account for additive effects when multiple phthalates modulate the same pathway. Such cumulative assessment of multiple biological parameters is more realistic, and offers the possibility of more accurately identifying the CMTA.     

Phthalate esters detected in various water samples and biodegradation of the phthalates by microbes isolated from river water

Phthalate esters (PEs), especially di-n-butyl phthalate (DBP) and di-(2-ethylhexyl) phthalate (DEHP) were detected in various water samples such as river water, well water and tap water. On degradation tests of PEs, Tempaku River water degraded almost 100% of diethyl phthalate (DEP), di-isobutyl phthalate and DBP, and approximately 70% of DEHP. All eight isolates from Tempaku River water (R1-R7, D1) did not degrade dimethyl phthalate (DMP), but showed biodegrading ability for the other PEs. The DBP-degrading ability was particularly high for the isolates R1-R3 and D1 of Acinetobacter iwoffii. Crude enzyme solutions prepared from bacterial cells of these isolates showed a higher degrading activity for DEHP compared with that for microbially-degradable DBP. Particularly high DEHP-degrading activity was found for crude enzyme solutions of the isolate D1. As metabolites from the river water and bacterial isolates, DMP and an unknown diester were produced from DEP. DMP, DEP, monomethyl phthalate, monobutyl phthalate (MBP) and an unknown diester were produced from DBP. DBP, DEP, DMP and an unknown diester were produced from DEHP. As metabolites by the crude enzyme solutions, DMP, MBP and an unknown diester derivative were produced from DBP. DBP, mono-(2-ethylhexyl) phthalate and an unknown diester derivative were produced from DEHP. Diesters with shortened alkyl carbon chains were also found as metabolites by the isolates and their crude enzyme solutions. The results suggest that the alkyl chains in the diesters are also decomposed in addition to monoester formation from DBP or DEHP at the first step reported for animals and some types of bacteria.     

Identification of the proximate peroxisome proliferator(s) derived from di (2-ethylhexyl) adipate and species differences in response.

Identification of the proximate peroxisome proliferator(s) derived from di (2-ethylhexyl) adipate (DEHA) has been achieved using primary hepatocyte cultures derived from different species and cyanide-insensitive fatty acyl CoA oxidase (PCO) as a marker enzyme for peroxisome proliferation. In rat and mouse hepatocytes, the parent compound (DEHA) had no effect on peroxisomal beta-oxidation, but primary metabolites of DEHA, mono (2-ethylhexyl) adipate (MEHA) and 2-ethylhexanol (EH), were approximately equipotent in PCO induction (5-fold at 0.5 mM final concentration). The secondary metabolite of DEHA, 2-ethylhexanoic acid (EHA), was in both species the most potent peroxisome proliferator (25- and 9-fold induction in mice and rats, respectively, at 1 mM final concentration). At 2 mM final concentration a tertiary metabolite of DEHA, 2-ethyl-5-hydroxyhexan-1-oic acid, was less effective in mouse and rat hepatocytes at inducing PCO (15- and 5-fold, respectively). 2-Ethyl-5-oxohexan-1-oic acid and 2-ethylhexan-1,6-dioic acid had little effect (2-3-fold in both rat and mouse hepatocytes). Thus, EHA was identified as the proximate peroxisome proliferator of DEHA and mouse hepatocytes were approximately twice as sensitive as rat hepatocytes to peroxisome proliferation due to MEHA, EH and EHA. We investigated further species differences in response to peroxisome proliferators by using guinea pig and marmoset primary hepatocyte culture. None of the chemicals studied stimulated peroxisomal beta-oxidation in these species up to a final concentration of 2 mM. Higher concentrations lead to cytotoxicity. This lack of sensitivity of guinea pig and marmoset hepatocytes is in agreement with previous studies with di (2-ethylhexyl) phthalate metabolites, suggesting the absence of a threat of hepatocarcinogenic damage to these species and confirming that primary hepatocytes cultures are useful models for investigating the phenomenon of peroxisome proliferation.     

Toxicity of di(2-ethylhexyl)phthalate (DEHP) and di(2-ethylhexyl)adipate (DEHA) under conditions of renal dysfunction induced with folic acid in rats: enhancement of male reproductive toxicity of DEHP is associated with an increase of the mono-derivative

F344 male rats were given five consecutive weekly subcutaneous injections of folic acid for induction of chronic renal dysfunction and then di(2-ethylhexyl)phthalate (DEHP) or di(2-ethylhexyl)adipate (DEHA) in the diet at a concentration of 0, 6000 or 25,000 ppm for 4 weeks in order to investigate whether male reproductive toxicity of the two chemicals might be enhanced under conditions of renal disease. Control animals also received DEHP or DEHA in the same manner but without folic acid pretreatment. Decreased testicular weights, seminiferous atrophy with vacuolization of sertoli cells and diminished sperm counts were more prominent in rats given folic acid and then 25,000 ppm DEHP as compared to those exposed to DEHP alone. No such reproductive toxicity was evident in rats given 6000 ppm DEHP or either dose of DEHA. An increased concentration of the mono-derivative of DEHP (mono(2-ethylhexyl)phthalate, MEHP) in the blood, testis and urine was considered relevant to the enhanced reproductive toxicity observed with DEHP.     

Induction of peroxisomal acyl CoA oxidase activity and lipid peroxidation in primary rat hepatocyte cultures

Peroxisome proliferators have been suggested to induce liver carcinogenesis as a result of increased peroxisomal hydrogen peroxide production and cellular oxidative stress. Primary monolayer cultures of hepatocytes isolated from male F344 rats were incubated in medium containing one of three different peroxisome proliferators and examined for the induction of peroxisomal CoA oxidase activity and lipid peroxidation. The latter parameter was determined by measuring levels of conjugated dienes in lipid fractions extracted from harvested cells. The peroxisome proliferators used in these studies were nafenopin and clofibric acid (two hypolipidemic drugs) and mono(2-ethylhexyl)phthalate (MEHP), the primary metabolite of the industrial plasticizer, di(2-ethylhexyl)phthalate (DEHP). The relative specific activity of peroxisomal acyl CoA oxidase was increased by about 300% after incubation for 44 h with 200 microM nafenopin; lower levels of induction were observed with clofibric acid or MEHP. Relative to controls, the level of conjugated dienes was increased approximately 2-fold after incubation with 200 microM nafenopin; there was no apparent increase in conjugated dienes after incubation with up to 200 microM MEHP or 400 microM clofibric acid. The increase in conjugated dienes with 200 microM nafenopin was inhibited by co-incubation with the antioxidant, N,N'-diphenyl-p-phenylenediamine. Thus, peroxisomal enzyme induction by nafenopin can result in membrane lipid peroxidation and monolayer cultures of rat hepatocytes may provide a useful model system for studying relationships between peroxisome proliferation, enhanced hydrogen peroxide production and cellular changes due to hepatic oxidative stress.     

Di(2-ethylhexyl)phthalate leached from medical PVC devices serves as a substrate and inhibitor for the P-glycoprotein

A di(2-ethylhexyl)phthalate (DEHP) was accidentally extracted from plastics in the process of purification of chemosensitizers reversing P-glycoprotein (Pgp)-mediated multidrug resistance (MDR). The purpose of this study was to investigate the Pgp-reversal activities of phthalates, which are endocrine-disrupting chemicals, by utilizing the Pgp-overexpressing leukemic cell line AML-2/D100. The phthalates includes DEHP, diethyl phthalate (DEP) and dibutyl phthalate (DBP). Of the tested phthalates, DEHP showed the highest Pgp-reversal activity and DEP the most potent drug-accumulating activity. On the other hand, they did not show any chemosensitizing activity against multidrug resistance associated protein-mediated MDR. The complete inhibition of Pgp by verapamil increased the cytotoxicity of DEHP, but neither DEP nor DBP had this effect, suggesting that DEHP alone may be a possible substrate for the Pgp. DEHP showed higher hydrophobicity than the other phthalates when determined by reverse phase-HPLC. In addition, DEHP, but not the others increased the ATPase activity in a concentration-dependent manner. This is the first report that phthalates can reverse Pgp-mediated MDR by increasing drug accumulation, as well as serving as substrates for the Pgp. It is thought that the hydrophobic characteristics of phthalates could play an important role in Pgp-inhibitory activity. Therefore, pharmaco- and toxicokinetic interactions between phthalates leached from medical PVC devices and substrates for the Pgp should be kept in mind.     

Antiandrogenic effects in male rats perinatally exposed to a mixture of di(2-ethylhexyl) phthalate and di(2-ethylhexyl) adipate

Di(2-ethylhexyl) phthalate (DEHP) is a well-known testicular toxicant inducing adverse effects in androgen responsive tissues. Therefore, di(2-ethylhexyl) adipate (DEHA) is currently being evaluated as a potential substitute for DEHP. Similarities in structure and metabolism of DEHP and DEHA have led to the hypothesis that DEHA can modulate the effects of DEHP. Wistar rats were gavaged with either vehicle, DEHP (300 or 750 mg/kg bw/day) or DEHP (750 mg/kg bw/day) in combination with DEHA (400 mg/kg bw/day) from gestation day (GD) 7 to postnatal day (PND) 17.

Decreased anogenital distance (AGD) and retention of nipples in male offspring were found in all three exposed groups. Dosed males exhibited decreased weights of ventral prostate and m. levator ani/bulbocavernosus. Histopathological investigations revealed alterations in testis morphology in both juvenile and adult animals. The litter size was decreased and postnatal mortality was increased in the combination group only, which is likely a combined effect of DEHP and DEHA. However, no combination effect was seen with respect to antiandrogenic effects, as males receiving DEHP in combination with DEHA did not exhibit more pronounced effects in the reproductive system than males receiving DEHP alone.     

Steroidogenesis in fetal male rats is reduced by DEHP and DINP, but endocrine effects of DEHP are not modulated by DEHA in fetal, prepubertal and adult male rats

The plasticizer di(2-ethylhexyl)phthalate (DEHP) exhibits antiandrogenic effects in perinatally exposed male rats. Di(2-ethylhexyl) adipate (DEHA) and diisononyl phthalate (DINP) are currently being evaluated as potential substitutes for DEHP, but similarities in structure and metabolism of DEHP with DEHA and DINP have led to the hypothesis that similarities in action may also exist. Pregnant Wistar rats were gavaged during gestation and lactation with vehicle, DEHP (300 or 750 mg/kg bodyweight per day), DINP (750 mg/kg bodyweight per day), DEHP (750 mg/kg bodyweight per day) in combination with DEHA (400 mg/kg bodyweight per day), or DEHP (300 mg/kg bodyweight per day) in combination with DINP (750 mg/kg bodyweight per day). DINP and DEHP were both shown to reduce testicular testosterone production ex vivo and testosterone levels in testes and plasma of male fetuses at gestation day 21, indicating a similar mechanism of action for DINP and DEHP. Additionally, plasma LH levels in male fetuses were elevated. Neonatal anogenital distance was reduced and the number of nipples at postnatal day 13 increased in DEHP-exposed male offspring. Serum inhibin B levels were significantly reduced in DEHP-exposed prepubertal male offspring, and in a few adult males. No modulating effects of DEHA on the endocrine effects of DEHP were detected, but a tendency towards an accumulating effect of DEHP and DINP in combination on suppression of testosterone synthesis was seen.