Apparent degradation of 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT) by a Cladosporium sp.

Cladosporium sp. strain AJR³18,501 was isolated from DDT-contaminated soil by its ability to decolourise the polymeric dye, Poly R-478. When inoculated into potato/dextrose broth containing 100 mg of DDT l^–1, a 21% decrease in DDT concentration was observed 12 days after its addition, however, no transformation products were detected by gas chromatography. TLC of culture medium and mycelia extracts revealed 1,1-dichloro-2,2-bis(p-chlorophenyl)ethane and five unknown transformation products associated with the mycelia.     

Thyroid disruptor 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT) prevents internalization of TSH receptor

The thyroid-stimulating hormone (TSH) receptor (TSHr) was made specifically fluorescent by insertion of a tetracysteine motif (TSHr-FlAsH) into the C-terminal end and transiently transfected into COS-7 and HeLa cells. The observation that TSH administration caused the intracellular level of cAMP to increase in both TSHr-FlAsH-transfected cell types indicated that the FlAsH binding motif did not alter normal TSHr functioning. When transfected into HeLa cells and stimulated with TSH, the TSHr-FlAsH receptor exhibited a pronounced perinuclear labelling pattern, whereas labelling remained on the cell surface following pre-incubation with 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT). Chinese hamster ovary (CHO)-TSHr cells probed with anti-TSHr antibodies were fluorescent mainly in the proximity of the plasma membrane, with fluorescence being primarily restricted to a juxta-nuclear position when exposed to 10 mU/ml TSH for 1 or 5 min. However, in the presence of DDT, the anti-TSHr fluorescence maintained a peripheral location along the cell plasma membrane, even if CHO-TSHr cells were stimulated with TSH for 1 and 5 min. To verify that DDT acted specifically on the TSHr, CHO cells transfected with the A₂a receptor were used as controls. Following a 1-min stimulation with 5’-(N-ethyl-carboxamido)-adenosine, A₂a receptors were gradually internalized regardless of the presence of DDT in the culture medium. Finally, immunoelectron microscopy of CHO-TSHr cells showed that a 1-min exposure to TSH sufficed to displace anti-TSHr antibodies tagged with 10-nm gold particles into coated pits and vesicles but that their superficial location was retained along the plasma membrane in the presence of DDT.     

Enhancement of hepatic microsomal drug oxidation and glucuronidation in rat by 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT)

A single dose of 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT) (160 mg/kg i.p.) enhanced the monooxygenase step of drug biotransformation in rat liver. The O-demethylation of p-nitroanisole was especially increased, a peak in activity approximately 5-fold compared with controls being attained in 7 days. On the other hand, there was only a 2-fold increase in aryl hydrocarbon hydroxylase activity.DDT increased the cytochrome P-450 content of the liver, this increase coincided well with that in p-nitroanisole O-demethylation activity.The UDPglucuronosyltransferase activity of liver microsomes was not enhanced by DDT administration, unless the microsomes were pretreated to reveal latent activity prior to assay. After trypsin digestion of microsomes a maximum increase in activity of approximately 3-fold was observed as a result of DDT dosage. The canonic surfactant cetylpyridinium chloride was less active in revealing the latent UDP-glucuronosyltransferase activity, and two other membrane perturbants, the detergent digitonin and phospholipase A, were unable to show enhancement in UDPglucuronosyltransferase as a result of DDT dosage.     

Interaction of the insecticide 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane with the beta-receptor adenylate cyclase system in Chang liver cell membranes

Interaction of the insecticide 1,1,1-trichloro-2,2-bis-(p-chlorophenyl)-ethane (DDT) with beta-receptor binding and adenylate cyclase activity of biological membranes has been studied. Following exposure of cultured Chang liver cells to DDT, maximal binding of the catecholamine antagonist [125I]-iodohydroxybenzylpindolol (HYP) to isolated cell membranes was decreased by 30% whereas the dissociation constant remained unchanged. Both basal activity and maximal isoproterenol-stimulated activity of adenylate cyclase were not altered. The isoproterenol concentration required for half-maximal stimulation of the enzyme was increased about 2-fold as was the agonist concentration required for half-maximal displacement of the antagonist HYP at the beta-receptor binding site. Thus, coupling efficiency of hormone-stimulated adenylate cyclase activity was not influenced by the presence of DDT in these membranes. The data show that interaction of DDT with the beta-receptor adenylate cyclase complex is restricted to the receptor component. Enzyme activity is directly linked to changes of agonist binding at the beta-receptor. Interference of DDT with signal transduction via 'fluidization' of membrane lipids has not been detected.     

Effects of dietary carbohydrate and myo-inositol on metabolic changes in rats fed 1,1,1-trichloro-2,2-bis (p-chlorophenyl) ethane (DDT)

This study was conducted to examine the effects of dietary carbohydrate [starch or sucrose (500 g/kg diet)] and myo-inositol (2 g/kg diet) on metabolic changes in rats fed 1,1,1-trichloro-2,2-bis (p-chlorophenyl) ethane (DDT) (0.7 g/kg diet). Dietary DDT enhanced serum and hepatic lipids and hepatic thiobarbituric acid reactive substances (TBA-RS), elevated hepatic activities of lipogenic enzymes such as malic enzyme (ME), glucose-6-phosphate dehydrogenase (G6PD) and fatty acid synthetase (FAS), increased hepatic cytochrome P-450 content and the activities of drug-metabolizing enzymes such as aminopyrine N-demethylase, glutathione S-transferase and 4-nitrophenol-UDP glucuronosyltransferase (4NP-UDPGT) and raised hepatic ascorbic acid and serum copper. Dietary sucrose promoted the increases in hepatic concentrations of total lipids, triglyceride and cholesterol, hepatic activity of ME, hepatic TBA-RS, cytochrome P-450 content and serum copper due to DDT feeding when compared to DDT administered in a starch based diet. Dietary myo-inositol significantly depressed the rises in hepatic concentrations of total lipids, triglyceride and cholesterol and the activities of ME and G6PD due to DDT feeding regardless of dietary carbohydrate quality. Dietary starch supplemented with myo-inositol potentiated the enhancements in hepatic activities of Phase II drug-metabolizing enzymes such as glutathione S-transferase and 4NP-UDPGT due to DDT feeding. These results suggest that dietary starch and myo-inositol can protect DDT fed rats against an accumulation of hepatic lipids, which might be mainly ascribed to the depression of hepatic lipogenesis. In addition, the present study implies that the supplementation of myo-inositol to high starch diet might improve the function of drug-metabolizing enzymes exposed to DDT.     

Studies on the Sites of Inhibition of Photosynthetic Electron Transport in Barley by DDT (1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane)

The effect of DDT in resistant and susceptible barley on variousphotosynthetic electron transport activities involving photosystems1 and 2 functioning alone and in series is reported. Whereasnone of the measured activities in resistant barleys were affectedby DDT treatment, in susceptible barley two sites of interactionof DDT with the photosynthetic electron transport chain weredemonstrated. The first site of inhibition was located beforephotosystem 2, between the sites of electron donation from diphenylcarbazideat pH 6·0 and 8·0, and on the oxidizing side ofthe inhibitions resulting from tris washing or heat treatment.Mn²⁺ ions, which can act as donor before photesystem 2, appearedto donate electrons on the H₂O side of the site of inhibitionby DDT. The second site of DDT inhibition was located in thepath of electron flow from photosystem 2 to NADP⁺ or diquat,and was demonstrated by using dichlorophenolindophenol and phenylenediaminesas electron donors.     

Metabolism of 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane and 1,1-dichloro-2,2-bis(p-chlorophenyl)ethane in the mouse

The metabolites of 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT) and 1,1-dichloro-2,2-bis(p-chlorophenyl)ethane (DDD) found in the urine of female Swiss mice are reported. The metabolites of DDT are DDD, 1-chloro-2,2-bis(p-chlorophenyl)ethene (DDMU), 1,1-dichloro-2,2-bis(p-chlorophenyl)ethene (DDE), 2,2-bis(p-chlorophenyl)acetic acid (DDA), 2-hydroxy-2,2-bis(p-chlorophenyl)acetic acid (αOH-DDA) and 2,2-bis(p-chlorophenyl)ethanol (DDOH), while DDD afforded DDMU, DDE, DDA, αOH-DDA and DDOH. The relative excreted levels of DDA and DDOH and the absence of 2,2-bis(p-chlorophenyl)acetaldehyde (DDCHO) are not consistent with the generally accepted path way for DDA formation, which involves sequential metabolism of DDT and DDD via DDOH to afford DDA. The quantitative results are interpreted to mean that DDA is formed by hydroxylation at the chlorinated sp³-side chain carbon of DDD to give 2,2-bis(p-chlorophenyl)acetyl chloride (DDA-Cl), which in turn is hydrolyzed to DDA. The excretion of αOH-DDA from both DDT- and DDD-treated mice has never been previously observed. It is suggested that this metabolite arises from the initial epoxidation of DDMU, a metabolite of DDT and DDD, to yield 1,2-epoxy-1-chloro-2,2-bis(p-chlorophenyl)ethane (DDMU-epoxide). This chloroepoxide is then hydrolyzed and oxidized to produce the αOH-DDA.     

Inhibition of Hill Reaction and Photophosphorylation by l,l,l-Trichloro-2,2-bis(p-chlorophenyl)ethane

The effect of DDT on DCIP and Fe(CN)₆^3– photoreductions,and cyclic and non-cyclic photo-phosphorylations, in some 30varieties of barley from widely different parts of the worldis reported. Whereas resistant barleys were not affected byDDT treatment, chloroplasts from treated susceptible barleysshowed parallel inhibitions of all the investigated aspectsof photosynthesis. However, in a few susceptible varieties inhibitionsof Fe(CN)₆^3– photoreduction or non-cyclic photophosphorylationwere not so pronounced. Possible reasons for these anomaliesare discussed; in particular earlier reports that DDT had noeffect on these latter photosynthetic activities may have beendue to the use of hypotonic media during chloroplast isolation.     

Effects of dietary myo-inositol, D-chiro-inositol and L-chiro-inositol on hepatic lipids with reference to the hepatic myo-inositol status in rats fed on 1,1,1-trichloro-2,2-bis (p-chlorophenyl) ethane

The effects of dietary 0.2% inositol stereoisomers on the hepatic lipids and myo-inositol (MI) status in rats fed with 1,1,1-trichloro-2,2-bis (p-chlorophenyl) ethane (DDT) were investigated. Dietary MI reduced the hepatic lipids in the rats fed with DDT. Dietary D-chiro-inositol (DCI) and L-chiro-inositol (LCI) both had a promoting effect on the increase in hepatic lipids due to DDT feeding. Dietary MI enhanced the hepatic free MI level and the phosphatidylinositol/phosphatidylcholine ratio, but dietary DCI reduced the level and ratio.     

The inhibition of 1,1,1-trichloro-2,2-bis-(p-chlorophenyl)ethane (DDT) dehydrochlorinase and gluthathione S-aryltransferase in grass-grub and housefly preparations

The inhibition of DDT [1,1,1-trichloro-2,2-bis-(p-chlorophenyl)ethane] dehydrochlorinase and glutathione S-aryltransferase by diphenylmethane and triphenylmethane derivatives was examined. Bis-(3,5-dibromo-4-hydroxyphenyl)methane and similar compounds were excellent inhibitors of both enzymes, but only DDT dehydrochlorinase was inhibited by compounds similar to bis-(N-dimethylaminophenyl)methane. Colour salts of the basic triphenylmethyl dyes were excellent inhibitors of both enzymes. All the inhibitors examined appeared to act by competition with glutathione for its binding site on the two enzymes.     

Bacterial and fungal cometabolism of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane (DDT) and its breakdown products.

Resting cells of bacteria grown in the presence of diphenylmethane oxidized substituted analogs such as 4-hydroxydiphenylmethane, bis(4-hydroxyphenyl)methane, bis(4-chlorophenyl)methane (DDM), benzhydrol, and 4,4'-dichlorobenzhydrol. Resting cells of bacteria grown with benzhydrol as the sole carbon source oxidized substituted benzhydrols such as 4-chlorobenzhydrol, 4,4'-dichlorobenzhydrol, and other metabolites of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane (DDT), such as DDM and bis(4-chlorophenyl)acetic acid. Bacteria and fungi converted 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane to 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene, 1,1-dichloro-2,2-bis(4-chlorophenyl)ethane, DDM, 4,4'-dichlorobenzhydrol, and 4,4'-dichlorobenzophenone. Aspergillus conicus converted 55% of bis(4-chlorophenyl)acetic acid to unidentified or unextractable water-soluble products. Aspergillus niger and Penicillium brefeldianum converted 12.4 and 24.6%, respectively, of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane to water-soluble and unidentified products. 4-Chlorophenylacetic acid, a product of ring cleavage, was formed from DDM by a false smut fungus of rice. A. niger converted 4,4'-dichlorobenzophenone to 4-chlorobenzophenone and a methylated 4-chlorobenzophenone.     

Liver enzyme induction by 1,1,1-trichloro-2,2-bis-(p-chlorophenyl)ethane (DDT) is accompanied by an increase in the specific activity of elongation factor 1.

Homogenates of liver were obtained from control rats and from rats that had received DDT [1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane]. The postmicrosomal supernatant fractions were used for the purification of elongation factor 1 by hydroxyapatite chromatography and phosphocellulose chromarography. The amount of binding factor present was essentially the same for both groups of animals, but the specific activity, as measured by the binding assay, was about twice as high in the DDT-treated preparations. After sucrose-gradient sedimentation, the difference in specific activity was found to reside in the low-molecular-weight (50000) form of elongation factor 1. The implications of an increased reactivity of elongation factor 1 during the induction of membrane enzymes are discussed.     

Bacterial and fungal cometabolism of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane (DDT) and its breakdown products

Resting cells of bacteria grown in the presence of diphenylmethane oxidized substituted analogs such as 4-hydroxydiphenylmethane, bis(4-hydroxyphenyl)methane, bis(4-chlorophenyl)methane (DDM), benzhydrol, and 4,4'-dichlorobenzhydrol. Resting cells of bacteria grown with benzhydrol as the sole carbon source oxidized substituted benzhydrols such as 4-chlorobenzhydrol, 4,4'-dichlorobenzhydrol, and other metabolites of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane (DDT), such as DDM and bis(4-chlorophenyl)acetic acid. Bacteria and fungi converted 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane to 1,1-dichloro-2,2-bis(4-chlorophenyl)ethylene, 1,1-dichloro-2,2-bis(4-chlorophenyl)ethane, DDM, 4,4'-dichlorobenzhydrol, and 4,4'-dichlorobenzophenone. Aspergillus conicus converted 55% of bis(4-chlorophenyl)acetic acid to unidentified or unextractable water-soluble products. Aspergillus niger and Penicillium brefeldianum converted 12.4 and 24.6%, respectively, of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane to water-soluble and unidentified products. 4-Chlorophenylacetic acid, a product of ring cleavage, was formed from DDM by a false smut fungus of rice. A. niger converted 4,4'-dichlorobenzophenone to 4-chlorobenzophenone and a methylated 4-chlorobenzophenone.