An alkaloid, two conjugate sesquiterpenes and a phenylpropanoid from Pachypodanthium confine Engl. and Diels

Two sesquiterpene-trimethoxystyrene conjugates (E)-1-[3'-(4',8'-dimethylnona-3',7'-dienyl)cyclohex-3'-enyl]-2,4,5-trimethoxybenzene (1) and (Z)-1-[3'-(4',8'-dimethylnona-3',7'-dienyl)cyclohex-3'-enyl]-2,4,5-trimethoxybenzene (2), a phenylpropanoid 1,2,4-trimethoxy-5-(1-methoxy-ethyl)-benzene (3), and an aporphine alkaloid N-acetylpachypodanthine (4), were isolated in addition to several known compounds from cyclohexane, dichloromethane and alkaloid extracts from bark of Pachypodanthium confine. The structures of these compounds were established based on the interpretation of their high resolution NMR (HSQC, HMBC, COSY and NOESY) spectral data.     

Effects of chemically induced maternal toxicity on prenatal development in the rat

The hypothesis that chemically induced overt maternal toxicity induces a characteristic syndrome of adverse developmental effects in the rat was investigated. Pregnant animals (Sprague-Dawley strain) were dosed by oral gavage with one of a series of compounds on days 6-15 of gestation. These chemicals were diquat (DIQ), ethylene-bis-isothiocyanate (EBIS), toxaphene (TOX), styrene (STY), 2,4-dichlorophenoxyacetic acid (2,4-D), 2,4,5-trichlorophenol (2,4,5-Tr), triphenyl tin hydroxide (TPTH), and cacodylic acid (CAC). The compounds were chosen because they exhibited little or no developmental toxicity in previous studies. Dosage levels producing maternal weight loss and/or lethality were determined from preliminary toxicity studies. Significant maternal weight reductions were noted during the course of treatment with all compounds except CAC and 2,4,5-Tr. Maternal lethality was produced by EBIS, TOX, 2,4,-D, and 2,4,5-Tr. The main treatment-related developmental toxicity noted in litters at term consisted of increased lethality (EBIS, TPTH) and decreased fetal weight (EBIS and CAC). Treatment-related anomalies were seen in litters treated with 2,4-D and TOX (supernumerary ribs) and with EBIS and STY (enlarged renal pelvis). No significant developmental effects were produced with DIQ, or 2,4,5-Tr. This study indicates that overt maternal toxicity as defined by weight loss or mortality is not always associated with the same defined syndrome of adverse developmental effects in the rat.     

The metabolism of γ-2,3,4,5,6-pentachlorocyclohex-1-ene and γ-hexachlorocyclohexane in rats

1. After intraperitoneal administration, gamma-hexachlorocyclohexane (Gammexane) and gamma-2,3,4,5,6-pentachlorocyclohex-1-ene were converted by rats into 2,3,5- and 2,4,5-trichlorophenol, which were excreted as free phenols and as sulphuric acid and glucuronic acid conjugates. 2. Derivatives of 2,4,5-trichlorophenol and 2,4,5-trichlorophenyl glucosiduronic acid and 2,4-dichlorophenylmercapturic acid were isolated from the urine as metabolites of gamma-2,3,4,5,6-pentachlorocyclohex-1-ene. 3. The phenolic metabolites of gamma-hexachlorocyclohexane and gamma-2,3,4,5,6-pentachlorocyclohex-1-ene isolated from urine were similar to those of 1,2,4-trichlorobenzene, which indicates that the two latter compounds are intermediates in gamma-hexachlorocyclohexane metabolism in rats.     

Degradation of the chlorinated phenoxyacetate herbicides 2,4-dichlorophenoxyacetic acid and 2,4,5-trichlorophenoxyacetic acid by pure and mixed bacterial cultures

Combined cell suspensions of the 2,4,5-trichlorophenoxyacetic acid (2,4,5-T)-metabolizing organism Pseudomonas cepacia AC1100, and the 2,4-dichlorophenoxyacetic acid (2,4-D)-metabolizing organism Alcaligenes eutrophus JMP134 were shown to effectively degrade either of these compounds provided as single substrates. These combined cell suspensions, however, poorly degraded mixtures of the two compounds provided at the same concentrations. Growth and viability studies revealed that such mixtures of 2,4-D and 2,4,5-T were toxic to AC1100 alone and to combinations of AC1100 and JMP134. High-pressure liquid chromatography analyses of culture supernatants of AC1100 incubated with 2,4-D and 2,4,5-T revealed the accumulation of chlorohydroquinone as an apparent dead-end catabolite of 2,4-D and the subsequent accumulation of both 2,4-dichlorophenol and 2,4,5-trichlorophenol. JMP134 cells incubated in the same medium did not catabolize 2,4,5-T and were also inhibited in initiating 2,4-D catabolism. A new derivative of strain AC1100 was constructed by the transfer into this organism of the 2,4-D-degradative plasmid pJP4 from strain JMP134. This new strain, designated RHJ1, was shown to efficiently degrade mixtures of 2,4-D and 2,4,5-T through the simultaneous metabolism of these compounds.     

Synthesis of D- and L-myo-inositol 2,4,5-trisphosphate and trisphosphorothioate: structural analogues of D-myo-inositol 1,4,5-trisphosphate

The preparation of D- and L-myo-inositol 2,4,5-trisphosphate is described, together with the phosphorothioate counterparts. The known chiral diols D- and L-1,4-di-O-benzyl-5,6-bis-O-p-methoxybenzyl-myo-inositol were regioselectively protected at the 3-position using a benzyl group via a 2,3-O-stannylene acetal. Removal of the p-methoxybenzyl groups of each enantiomer gave D- and L-1,3,6-tri-O-benzyl-myo-inositol. Phosphitylation with bis(benzyloxy)diisoproplyaminophosphine and 1H-tetrazole gave the trisphosphite intermediate for each enantiomer. Oxidation with 3-chloroperoxybenzoic acid gave the fully protected D- and L-myo-inositol 2,4,5-trisphosphates. Sulphoxidation of the D- and L-2,4,5-trisphosphite intermediates gave the fully protected D- and L-myo-inositol 2,4,5-trisphosphorothioate compounds. The fully protected trisphosphates were deblocked using hydrogenolysis and the phosphorothioates were deprotected using sodium in liquid ammonia. The individual compounds were then purified using ion exchange chromatography to afford pure D- and L-myo-inositol 2,4,5-trisphosphates together with the corresponding phosphorothioates.     

Degradation of the chlorinated phenoxyacetate herbicides 2,4-dichlorophenoxyacetic acid and 2,4,5-trichlorophenoxyacetic acid by pure and mixed bacterial cultures.

Combined cell suspensions of the 2,4,5-trichlorophenoxyacetic acid (2,4,5-T)-metabolizing organism Pseudomonas cepacia AC1100, and the 2,4-dichlorophenoxyacetic acid (2,4-D)-metabolizing organism Alcaligenes eutrophus JMP134 were shown to effectively degrade either of these compounds provided as single substrates. These combined cell suspensions, however, poorly degraded mixtures of the two compounds provided at the same concentrations. Growth and viability studies revealed that such mixtures of 2,4-D and 2,4,5-T were toxic to AC1100 alone and to combinations of AC1100 and JMP134. High-pressure liquid chromatography analyses of culture supernatants of AC1100 incubated with 2,4-D and 2,4,5-T revealed the accumulation of chlorohydroquinone as an apparent dead-end catabolite of 2,4-D and the subsequent accumulation of both 2,4-dichlorophenol and 2,4,5-trichlorophenol. JMP134 cells incubated in the same medium did not catabolize 2,4,5-T and were also inhibited in initiating 2,4-D catabolism. A new derivative of strain AC1100 was constructed by the transfer into this organism of the 2,4-D-degradative plasmid pJP4 from strain JMP134. This new strain, designated RHJ1, was shown to efficiently degrade mixtures of 2,4-D and 2,4,5-T through the simultaneous metabolism of these compounds.     

Regulation of 2,4,5-trichlorophenoxyacetic acid and chlorophenol metabolism in Pseudomonas cepacia AC1100

The expression of the degradative genes encoding 2,4,5-trichlorophenoxyacetic acid (2,4,5-T), 2,4,5-trichlorophenol (2,4,5-TCP), and pentachlorophenol (PCP) dechlorination in a 2,4,5-T-degrading strain of Pseudomonas cepacia was examined during growth on alternate carbon sources. The dechlorination mechanisms for all three compounds were expressed in 2,4,5-T- and 2,4,5-TCP-grown cells but were not expressed in cells grown on succinate, glucose, or lactate. The addition of 2,4,5-TCP or PCP to cells grown on succinate or lactate resulted in the expression of the 2,4,5-TCP dechlorination mechanism in resting cells after 1-h lag. This expression was prevented by the presence of chloramphenicol in the resting cell suspension. Succinate-plus-PCP-grown resting cells preincubated with 2,4,5-TCP fully induced the trichlorophenol dechlorination system and partially induced the PCP dechlorination system. Preincubation of succinate-plus-PCP-grown resting cells with PCP induced neither the 2,4,5-TCP nor the PCP dechlorinating system. Succinate-grown resting cells converted 2,4,5-T to 2,4,5-TCP even in the presence of chloramphenicol. Thus, the data indicate that the enzyme(s) which converts 2,4,5-T to 2,4,5-TCP is constitutively expressed, whereas those that convert 2,4,5-TCP to central intermediates are induced by 2,4,5-TCP but not by 2,4,5-T or PCP and are repressed in the presence of an alternate carbon source.     

Regulation of 2,4,5-trichlorophenoxyacetic acid and chlorophenol metabolism in Pseudomonas cepacia AC1100.

The expression of the degradative genes encoding 2,4,5-trichlorophenoxyacetic acid (2,4,5-T), 2,4,5-trichlorophenol (2,4,5-TCP), and pentachlorophenol (PCP) dechlorination in a 2,4,5-T-degrading strain of Pseudomonas cepacia was examined during growth on alternate carbon sources. The dechlorination mechanisms for all three compounds were expressed in 2,4,5-T- and 2,4,5-TCP-grown cells but were not expressed in cells grown on succinate, glucose, or lactate. The addition of 2,4,5-TCP or PCP to cells grown on succinate or lactate resulted in the expression of the 2,4,5-TCP dechlorination mechanism in resting cells after 1-h lag. This expression was prevented by the presence of chloramphenicol in the resting cell suspension. Succinate-plus-PCP-grown resting cells preincubated with 2,4,5-TCP fully induced the trichlorophenol dechlorination system and partially induced the PCP dechlorination system. Preincubation of succinate-plus-PCP-grown resting cells with PCP induced neither the 2,4,5-TCP nor the PCP dechlorinating system. Succinate-grown resting cells converted 2,4,5-T to 2,4,5-TCP even in the presence of chloramphenicol. Thus, the data indicate that the enzyme(s) which converts 2,4,5-T to 2,4,5-TCP is constitutively expressed, whereas those that convert 2,4,5-TCP to central intermediates are induced by 2,4,5-TCP but not by 2,4,5-T or PCP and are repressed in the presence of an alternate carbon source.     

Phenyl indane from acorus calamus

Besides three known compounds, two new compounds, namely Z-3-(2,4,5-trimethoxy phenyl)-2-propenal and a new phenyl indane have been isolated from the rhizomes of Acorus calamus. These compounds have been characterized from their spectral data and by synthesis.     

Degradation of halogenated aromatic compounds

Due to their persistence, haloaromatics are compounds of environmental concern. Aerobically, bacteria degrade these compounds by mono- or dioxygenation of the aromatic ring. The common intermediate of these reactions is (halo)catechol. Halocatechol is cleaved either intradiol (ortho-cleavage) or extradiol (meta-cleavage). In contrast to ortho-cleavage, meta-cleavage of halocatechols yields toxic metabolites. Dehalogenation may occur fortuitously during oxygenation. Specific dehalogenation of aromatic compounds is performed by hydroxylases, in which the halo-substituent is replaced by a hydroxyl group. During reductive dehalogenation, haloaromatic compounds may act as electron-acceptors. Herewith, the halosubstituent is replaced by a hydrogen atom.Abbreviations CBz chlorobenzene - DCBz dichlorobenzene - TrCBz trichlorobenzene - TCBz tetrachlorobenzene - PCBz pentachlorobenzene - HCBz hexachlorobenzene - CBA chlorobenzoic acid - BBA bromobenzoic acid - FBA fluorobenzoic acid - IBA iodobenzoic acid - CP chlorophenol - CA chloroaniline - PCBs polychlorinated biphenyls - CB chlorobiphenyl - 2,4-D 2,4-dichlorophenoxyacetic acid - 2,4,5-T 2,4,5-trichlorophenoxyacetic acid     

Testing of 2,4,5-T-amino acid conjugates for mutagenic activity in Salmonella typhimurium strains

Since amino acid conjugates are plant metabolites of the herbicide 2,4,5-trichlorophenoxyacetic acid (2,4,5-T), 5 amino acid conjugates (aspartic acid, glutamic acid, leucine, methionine and tryptophan) of 2,4,5-T were tested for possible mutagenic activity utilizing 5 strains of Salmonella typhimurium (TA97, TA98, TA100, TA1535 and TA1538) with and without rat-liver microsomal and cytosolic enzymes. These compounds did not cause any significant increase in reversions when compared with controls in the presence or absence of the activating system. Further, linear regression analysis showed no significant (p less than 0.05) dose-response relationships. Thus, it was concluded that the tested amino acid conjugates of 2,4,5-T are not mutagens or promutagens in these assays.     

Comparison of the effect of phenoxyherbicides on human erythrocyte membrane (in vitro)

The molecular mechanisms of phenoxyherbicides action in animals have been insufficiently studied. Now, we have investigated the interaction of sodium salts of phenoxyherbicides, e.g., 2,4-dichlorophenoxyacetic acid (2,4-D-Na), 2,4,5-trichlorophenoxyacetic acid (2,4,5-T-Na) and 4-chloro-2-methylphenoxyacetic acid (MCPA-Na) with human erythrocytes. In this study, we evaluated the effect of these compounds on erythrocyte membrane fluidity as well as changes in membrane proteins content. It was observed that all of the compounds studied altered membrane fluidity, changed the size and shape of the erythrocytes and provoked echinocytes formation. It was also revealed that 2,4-D-Na and 2,4,5-T-Na changed the content of erythrocyte membrane proteins mainly by a decrease in the level of spectrin and low molecular weight proteins. The comparison of the action of phenoxyherbicides examined showed that 2,4,5-T-Na caused the greatest changes in the erythrocytes membrane, whereas MCPA-Na induced the lowest alterations in the incubated cells. It must be noted that changes of the investigated parameters were observed only at presence of significant concentrations of these compounds that may penetrate human organism only as a result of acute poisoning.     

Two New Norlignans and a New Lignanamide from Peperomia tetraphylla

Two new cyclobutane-type norlignans, methyl rel-(1R,2S,3S)-2-(7-methoxy-1,3-benzodioxol-5-yl)-3-(2,4,5-trimethoxyphenyl)cyclobutanecarboxylate (1), and methyl rel-(1R,2R,3S)-2-(7-methoxy-1,3-benzodioxol-5-yl)-3-(2,4,5-trimethoxyphenyl)cyclobutanecarboxylate (2), and a new lignanamide, 3-hydroxy-N-[2-(4-hydroxyphenyl)ethyl]-α-[4-(2-{N-[2-(4-hydroxyphenyl)ethyl]carbamoyl}ethenyl)-3-methoxyphenoxy]-4-methoxycinnamamide 4,8″-ether (3), along with five known amides, 4-8, were obtained from the whole plant of Peperomia tetraphylla. Their structures were elucidated mainly by the analysis of NMR and MS data. The new compounds 1-3 and the known compound 4 were tested for their cytotoxic activities against the HepG2 (human hepatocarcinoma), A549 (human lung cancer), and HeLa (human cervical cancer) cell lines. Compound 4 showed significant cytotoxicity against HepG2 cell lines with an IC(50) value of 9.4 ± 1.0?μM.     

Metabolism of synthetic inositol trisphosphate analogs

A series of synthetic analogs was employed to explore structure-activity relationships in the metabolism of the second messenger inositol trisphosphate (IP3) in vascular tissue. Cytosolic IP3-5-phosphatase activity was purified approximately 240-fold from bovine aorta. All synthetic analogs tested were apparent competitive inhibitors of the 5-phosphatase activity. The order of potency was DL-1,3,4,5-IP3 greater than D-1,4,5-IP3 greater than DL-1,3,4-IP3 greater than L-1,4,5-IP3 greater than 1,3,5-IP3 greater than DL-6-methoxy-1,4,5-IP3 greater than DL-2,4,5-IP3 greater than DL-1,2,4-cyclohexane-P3. The least potent analogs had Ki values only 11 times higher than the apparent Km of the substrate D-1,4,5-[3H]IP3. However, only three synthetic compounds, DL-1,3,4,5-IP4, D-1,4,5-IP3, and DL-2,4,5-IP3, could serve as substrates for the 5-phosphatase. IP3 kinase activity in the same tissue exhibited considerably more selectivity with respect to inhibition by IP3 analogs. D-1,4,5-IP3 was about 30 times more potent than DL-1,3,4,5-IP4 and 100-1000 times more potent than the other compounds tested. The function of the IP3 receptor was evaluated by measuring labeled calcium mobilization in permeabilized bovine aortic smooth muscle cells in culture. While all analogs tested were full agonists, vast differences in potency were observed. D-1,4,5-IP3 was about 30 times more potent than DL-2,4,5-IP3 and 100-2000 times more potent than the other analogs tested. The results suggest that IP3-5-phosphatase activity is relatively nonselective in the binding of inositol polyphosphates, while IP3 kinase activity and the IP3 receptor exhibit great selectivity in the recognition of these compounds.     

DNA-binding,enzyme inhibition,and photochemical properties of chalcone-containing metallophthalocyanine compounds

In this study, two novel phthalocyanine complexes were synthesized using their corresponding metal salts and 4-(4-(3-(2,4,5-trimethoxyphenyl)acryloyl)phenoxy)phthalo-nitrile as chalcone ligand (4), which was prepared from the reaction of 4-nitrophthalonitrile with 4-hydroxyphenyl-3-(2,4,5-trimethoxyphenyl)prop-2-en-1-one (3). These metallophthalocyanines showed good solubility in organic solvents such as CDCl₃, DCM, THF, DMF, and DMSO. The novel phthalocyanine compounds 4a (Pc-Zn) and 4b (Pc-Co) were characterized using their UV–vis, FT-IR, ¹H NMR, ¹³C NMR, and MALDI-TOF mass spectra and elemental analysis. Then the DNA-binding and xanthine oxidase and carbonic anhydrase-I inhibition properties of compounds 4a and 4b were investigated. Photochemical properties (such as singlet oxygen generation and photodegradation) of this novel chalcone phthalocyanine (4a) were determined in dimethyl sulfoxide (DMSO).     

Synthesis and antioxidant, cytotoxicity and antimicrobial activities of novel curcumin mimics

Claisen-Schmidt condensation of 3-(1,2,3,6-tetrahydro-1-methylpyridin-4-yl)-2,4,5- trimethoxybenzaldehyde 3 and various aromatic, heterocyclic and alicyclic amides of 3- aminoacetophenone 6(a-s) afforded novel curcumin mimics. All the synthesized compounds were characterized by IR, (1)H NMR, Mass spectroscopy and evaluated for antioxidant, cytotoxicity and antimicrobial activity. Out of the 20 compounds screened, compounds 7i, 7l, 7q, and 7n have shown excellent radical scavenging activity, compounds 7o, 7t, 7f, and 7r have shown significant xanthine oxidase inhibition, and compounds 7a, 7k and 7l were found to be potent inhibitors of selected cancer cell lines. Compounds 7h, 7t, 7l, 7i, and 7e have shown good antibacterial activity, whereas compounds 7j, 7f, 7o, 7h, and 7t exhibited significant antifungal activity.     

Alterations in cholesterol and fatty acid biosynthesis in rat liver homogenates by aryloxy acids (Short Communication)

2,4-Dichlorophenoxyacetic acid and 2,4,5-trichlorophenoxyacetic acid inhibited the incorporation of [2-(14)C]mevalonate into cholesterol and non-saponifiable lipids. Both compounds inhibited the conversion of [1-(14)C]isopentenyl pyrophosphate into cholesterol and the synthesis of cholesterol and fatty acids from [2-(14)C]acetate. There was no inhibition of the conversion of [1-(14)C]mevalonate into CO(2). At low concentrations (0.5mm) of the compounds there was a stimulation of acetate incorporation into fatty acids.     

Immunoprecipitation of pyrimidine(6-4)pyrimidone photoproducts and cyclobutane pyrimidine dimers in uv-irradiated DNA

Biological studies suggest that a significant proportion of the cytotoxicity observed in mammalian cells after uv irradiation may be due to damage other than cyclobutane dimers in DNA. Although pyrimidine-pyrimidone (6-4) photoproducts have been implicated as major contributors to cell lethality, their induction has been measured at considerably less than cyclobutane pyrimidine dimers when measured by chromatographic techniques. Because the yield of (6-4) photoproducts may be reduced by their lability to extreme heat and pH, we have advised an alternative, immunological quantification which does not require DNA hydrolysis. Affinity-purified rabbit antisera were used to precipitate low molecular weight 32P-labeled PM2 DNA irradiated with increasing fluences of uv light. DNA of known molecular weight was used to determine rates of induction for antibody-binding sites associated with (6-4) photoproducts and cyclobutane dimers. These rates were calculated to be 0.6 (6-4) photoproducts and 1.2 cyclobutane dimers/10(8) Da/J/m2. At low uv fluences (6-4) photoproducts were induced at one-half the rate of cyclobutane dimers, whereas at higher fluences (6-4) photoproducts predominated.     

Biodegradation of 2,4,5-trichlorophenol by aerobic microbial communities: biorecalcitrance,inhibition, and adaptation

Chlorinated aromatic compounds challenge our environment and wastewater treatment processes due to their biorecalcitrance and inhibition. In particular, 2,4,5-trichlorophenol (TCP) seems to demonstrate greater resistance to biodegradation than other trichlorophenols and is a known uncoupler of the electron transport chain, although little work addresses this compound specifically. Here, we investigate the biorecalcitrance, inhibition, and adaptation to 2,4,5-trichlorophenol by aerobic mixed microbial communities. We show that 2,4,5-trichlorophenol is strongly resistant to biodegradation at concentrations greater than 40 μM, demonstrates inhibition to respiration in direct proportion to 2,4,5-trichlorophenol concentration (with 50% inhibition projected near 85 μM 2,4,5-trichlorophenol), and does not sustain biomass in continuous reactors, even when all input 2,4,5-trichlorophenol is degraded. Communities showed consistent adaptation patterns to 2,4,5-trichlorophenol at concentrations of 10 μM and 20 μM, but these patterns diverged at concentrations greater than 40 μM. Finally, thermodynamic approximations were used to estimate the yield of 2,4,5-trichlorophenol as 0.165 gVSS/gCOD, a low value that partially explains why biodegradation of 2,4,5-trichlorophenol did not sustain the biomass. In particular, we estimated that the minimum concentration to support steady-state biomass (S _min) is approximately 180 μM, a value much larger than the 40-μM concentration that is strongly resistant to biodegradation. Thus, readily biodegradable concentrations of 2,4,5-trichlorophenol are too low to sustain the biomass that biodegrades it.     

Morphological transformation and catalase activity of syrian hamster embryo cells treated with hepatic peroxisome proliferators,TPA and nickel sulphate

The abilities of the hepatic peroxisome proliferators (HPPs) clofibrate, di(2-ethylhexyl)phthalate (DEHP), mono(2-ethylhexyl)- phthalate (MEHP), 2,4-dichlorophenoxy acetic acid (2,4-D), 2,4,5-trichlorophenoxy acetic acid (2,4,5-T) and tiadenol to induce morphological transformation and to increase the catalase activity of Syrian hamster embryo (SHE) cells were studied. DEHP, MEHP, clofibrate and tiadenol induced morphological transformation of SHE cells and increased the catalase activity. DEHP was more potent than clofibrate and tiadenol in both inducing catalase and morphological transformation, while MEHP seemed more potent than DEHP in inducing catalase, but not morphological transformation, 2,4,5-T and 2,4-D did not induce morphological transformation, but 2,4,5-T was more potent than clofibrate in increasing the catalase activity. These results show that several HPPs induce morphological transformation of SHE cells and an increase in the catalase activity. There is, however, no direct connection between these two parameters, as seen from the results of 2,4,5-T. The tumor promoter TPA, and the metal salt nickel sulphate, induced morphological transformation of SHE cells without any appreciable increase in the catalase activity. These results further corroborate the dissociation between induction of morphological transformation and the increase in catalase activity.Abbreviations Clofibrate ethyl-2-(p-chlorophenox) isobutyrate - 2,4-D 2,4-dichlorophenoxy acetic acid - DEHP di(2-ethylhexyl)phthalate - HPP hepatic peroxisome proliferator - MEHP mono(2-ethylhexyl)phthalate - SHE Syrian hamster embryo - 2,4,5-T 2,4,5-trichlorophenoxy acetic acid - tiadenol di(hydroxyethylthio)-1,10-decane