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EFFECTS OF DIELDRIN, PICROTOXIN AND TELODRIN ON THE METABOLISM OF AMMONIA IN BRAIN.

1. Increases in the concentrations of lactic acid and pyruvic acid in rat brain during acute dieldrin poisoning are associated with hyperactivity of the brain, whereas an increase in the cerebral alanine concentration occurs before the convulsions. Throughout the dieldrin-induced seizure pattern, fluctuations in the concentration of brain ammonia are out of phase with the actual convulsions. 2. Increases in the concentrations of alanine, ammonia and lactic acid in rat brain accompany picrotoxin-induced seizures; there is no increase in the concentration of glutamine. These changes are consistent with the inhibition of glutamine synthesis. 3. In addition to previously reported changes in the concentrations of intermediary metabolites of the brain after the administration of Telodrin (Hathway & Mallinson, 1964), increases have now been found in the alanine and lactic acid concentrations. Since increases in the alanine and glutamine concentrations occur before the convulsions, liberation of ammonia also occurs before the onset of convulsions and throughout their course. Ammonia-binding mechanisms later become inadequate and free ammonia accumulates in cerebral tissues. 4. An increase in the pyruvic acid concentration of the brain after the intraperitoneal injection of either dieldrin or Telodrin is endogenous in origin. 5. The parenteral administration of a small dose of glutamine increases the cerebral concentrations of alanine and glutamic acid. Some animals previously treated with glutamine resisted Telodrin convulsions. 6. Mechanisms for the disposal of ammonia liberated in brain are discussed.

Alanine↗

Dieldrin-induced mallory bodies in hepatic tumors of mice of different strains.

Mallory bodies (MBs) were induced in hepatic tumors by administration for up to 85 weeks of a diet containing 10 ppm dieldrin to 50 C3H/He and 62 C57BL/6J x C3H/He B6C3F1 male mice. MBs were seen in 15 of 28 (54%) mice which developed benign hepatic tumors and 33 of 45 (73%) mice with hepatocellular carcinoma, but in only 3 of 39 (8%) mice without hepatic tumors. In mice with tumors, the MBs were predominantly confined to tumor tissue and persisted in a carcinoma transplanted into a nude mouse. MBs were not observed, however, in hepatic tumors of 67 C57BL/6J, 49 C3H/He, or 81 B6C3F1 mice given 12 micrograms diethylnitrosamine i.p. on Days 0, 3, 9, and 15. Thirty-one of 195 control mice of all three strains had hepatic tumors. Only one of the controls had a tumor with an MB, and no MBs were seen in nontumor-bearing livers of controls animals. These observations, coupled with the results of a previous study in which MBs were observed in hepatocytes of dieldrin-treated C57BL/6J mice, indicate that mice treated with dieldrin are a reliable animal model for the study of MBs.

Animals↗

Exposure to low doses of the environmental chemical dieldrin causes behavioral deficits in animals prevented from coping with stress.

Experiments were conducted which assessed the effects of low doses of an environmental contaminant in conjunction with various forms of stress. Rats were given acute doses (0, 0.5, 1.5, 4.5 mg/kg) of the chemical dieldrin and subsequently exposed to a series of 40 escapable shocks, identical inescapable shocks, or no shock in an operant chamber. Eight hours later, the subjects were re-exposed in a shuttlebox to footshock which was escapable upon performance of an FR-2 shuttle response. Escape deficits which were related in magnitude to the size of the dieldrin dose were found in the inescapable shock group but not in the escapable shock or no shock groups. The data suggest that experience with the lack of control over stress is critical in determining the behavioral effects of the agent and that the behavioral effects caused by uncontrollable stress may be exacerbated by concurrent exposure to such compounds. These results are discussed in terms of previous studies on the behavioral actions of dieldrin, the response to uncontrollable stress and the common neuronal systems that may be involved.

Animals↗

Transport of dieldrin between air and water.

The transfer rate of dieldrin from water to air has been measured in a wind tunnel yielding transfer velocities in the range 2.6 x 10(-5) to 1.5 x 10(-4) cm s-1. The transfer rate from air to water was measured with a wetted-wall column and gave transfer velocities in the range 9 x 10(-3) to 5 x 10(-2) cm s-1. An analysis of the data showed that processes in the liquid phase offered no larger resistance to the transfer of dieldrin between air and water than processes in the gas phase. The results are considered in relation to the transfer of dieldrin between the atmosphere and the ocean surface layer.

Air Movements↗

A case-control study of persons with elevated blood levels of dieldrin.

Twenty-seven pesticide workers with elevated blood levels of dieldrin (greater than or equal to 15 ppb) were involved in a case-control study which included history and physical examination, comprehensive neurological evaluation, laboratory tests, and psychological and psychomotor testing. No clinically important differences were found on history, physical, specialized neurological tests, or laboratory examination. The exposed group showed a statistically significant difference in five out of 58 psychological (P) and psychomotor (PM) tests--at least three would be expected by chance (p less than or equal to .05). In only one of these tests was there any significant correlation with dieldrin levels. Even though the exposed group had worse scores than the control group in 47 of 58 P--PM tests, such scores were, with a few exceptions, in the normal range of values. Elevated blood levels of dieldrin encountered in this study do not appear to have any chronic deleterious effects on health, as measured by conventional medical work-up and extensive central nervous system testing.

Brain↗

Effect of dieldrin on the stability of lysosomes in the rat liver.

The effect of dieldrin on the bound and free activity of cathepsin, acid ribonuclease, acid phosphatase and aryl sulphatase has been investigated. Administration of dieldrin increased the activity of free cathepsin, acid ribonuclease, and acid phosphatase in rat liver whereas it did not affect the activity of aryl sulphatase. This indicates that dieldrin labilizes the lysosomes.

Acid Phosphatase↗

Blocking actions of BIDN, a bicyclic dinitrile convulsant compound, on wild-type and dieldrin-resistant GABA receptor homo-oligomers of Drosophila melanogaster expressed in Xenopus oocytes.

The receptor antagonist actions are described for a novel bicyclic dinitrile compound (BIDN, 3,3-bis-(trifluoromethyl)-bicyclo [2.2.1] heptane-2,2-dicarbonitrile) on a Drosophila melanogaster homo-oligomeric GABA receptor expressed in Xenopus oocytes. BIDN blocked the wild-type form of the receptor in a neither purely competitive, nor purely non-competitive manner, being dependent on the GABA concentration yet insurmountable, and block was independent of the membrane potential. BIDN was found to be less effective against a mutant (A(302) --> S) form of the receptor resistant to dieldrin and picrotoxinin. This cross resistance of dieldrin-resistant receptors to BIDN is of interest in the light of recent findings that BIDN binding to insect membranes is displaced competitively by dieldrin, but not by picrotoxinin.

Animals↗

Excitatory and depressant effects of dieldrin and aldrin-transdiol in the spinal cord of the toad (Xenopus laevis).

An investigation was made into the action of the insecticide dieldrin and one of its metabolites, aldrin-transdio, on the isolated spinal cord of the toad, Xenopus laevis. Conventional electrophysiological techniques were used for stimulating and recording of dorsal and ventral spinal roots. An augmentation of polysynaptic reflex activity along with a marked reduction of orthodromic postsynaptic inhibition could be demonstrated in preparations isolated from dieldrin-poisoned animals. However, application of dieldrin to the isolated spinal cord failed to produce any significant effect. Application of aldrin-transdiol, on the other hand, caused a potentiation of spinal reflex activity and an increase in spontaneous activity of ventral and dorsal roots. Aldrin-transdiol also produced a marked reduction of spinal inhibitory mechanisms. The excitatory effects of aldrin-transdiol were followed by a strong depressant action on spinal excitability.

Aldrin↗

Levels of aldrin and dieldrin in environmental samples from Delhi, India.

Aldrin and dieldrin residues in soil, earthworms, water, fish and clams from different sites in Delhi were monitored. Concentrations of aldrin and dieldrin were found to be higher in earthworms than in soil. Concentrations of dieldrin were higher in fish than the ambient water, but the concentration of aldrin in the ambient water was the same as that in fish and clams.

Aldrin↗

Substrate-affinity relationship of succinate dehydrogenase in brain of albino rat during dieldrin toxicity.

Substrate kinetics of succinate dehydrogenase (EC 1.3.99.1) were studied in the brain of control and dieldrin-treated albino rats. Dieldrin inhibited the enzyme activity to various degrees and also altered the Michaelis-Menten constant (Km) of the enzyme. Activation energy values (delta E) were increased, suggesting decreased maximal velocity Vmax, and the high Km obtained for the enzyme also revealed decreased enzyme-substrate affinity and masking of active sites by dieldrin.

Animals↗

No effect of dieldrin on progesterone production in gilts.

The effect of feeding pigs with dieldrin containing feed on the progesterone profile of the estrous cycle was investigated. Eight gilts comprising three controls and five treatment animals were given feed containing 40 ppm of dieldrin for 60 days. Dieldrin levels in mg/kg fat in tissues analysed were; fat 15.15, muscle 18.68, liver 12.21, corpus luteum 13.68, kidney 14.16, serum 2.84 and brain 1.66. On analysing serum progesterone levels no significant difference (P > 0.10) between the progesterone profile of the control and the treatment animals was observed.

Animals↗

Comparative study of dieldrin effects on amphibian liver and early embryo phospholipids.

1. The effect of Dieldrin on phospholipid content and composition was compared in adult frog liver and in early embryos. 2. Male frogs are more resistant to acute Dieldrin treatment than females. Total phospholipids content increases in the liver of male animals while in females decreases. 3. Early embryo development was not affected morphologically by the addition of 0.02-10.0 mg of Dieldrin/1; however phospholipid content and composition was altered. 4. Adaptive changes in the embryo due to chronically administered Dieldrin is suggested.

Animals↗

Factors in the accumulation of dieldrin in broiler organs: quantity ingested, sex and weight of animal.

The effect of several factors in relation to the quantities of dieldrin accumulated in different organs of broilers was studied. Feedstuff was contaminated at doses of 60, 90, 120, 200 and 240 ppm. With the doses used, the results show an accumulation summit over which the amounts accumulated are not affected by greater quantities of dieldrin ingested. The accumulation of dieldrin in the female is greater than in the male and the weight of the animal does not significantly affect the response.

Animals↗

Exposure to p,p'-DDE or dieldrin during the reproductive season alters hepatic CYP expression in largemouth bass (Micropterus salmoides).

Largemouth bass (LMB) in Central Florida living on sites with high levels of organochlorine pesticides (OCPs) have exhibited poor reproductive success and altered steroid profiles. The mechanism underlying these changes is unknown, however changes in the rate of steroid metabolism could alter steroid homeostasis. Members of the CYP2 and CYP3A families play a significant role in the metabolism of many xenobiotics and endogenous compounds, including sex steroids. Therefore, the goal of this study was to identify members of the CYP2 and CYP3A families in LMB and characterize the effects of OCP exposure on their expression. Full-length clones of two CYP3A isoforms were obtained from LMB liver, CYP3A68 and 3A69, which exhibited significant sequence divergence. Full-length clones for CYP2N14 and CYP2P11 were also obtained from LMB liver. Steady-state mRNA levels of each of these CYPs increased in both sexes between early reproductive phase (December) and peak reproductive phase (March). Expression of CYP3A68 and CYP2P11 was sexually dimorphic during peak reproductive phase with 2-fold higher expression in females and males, respectively. Foodborne exposure to 46 ppm p,p'-DDE or 0.8 ppm dieldrin for 30 days did not have a significant effect on expression of CYPs. However, 4 months exposure to p,p'-DDE induced CYP3A68 and 3A69 expression in both sexes, while dieldrin produced weak induction of CYP3A68 and suppressed CYP3A69 expression in females, but had no effect on males. Neither p,p'-DDE nor dieldrin significantly altered the expression of CYP2P11 or CYP2N14. This work demonstrates that there are significant changes in CYP expression that occur during LMB reproduction which can be modified by exposure to OCPs.

Amino Acid Sequence↗

Dieldrin-induced neurotoxicity: relevance to Parkinson's disease pathogenesis.

Parkinson's disease (PD) is increasingly recognized as a neurodegenerative disorder strongly associated with environmental chemical exposures. Recent epidemiological data demonstrate that environmental risk factors may play a dominant role as compared to genetic factors in the etiopathogenesis of idiopathic Parkinson's disease. Identification of key genetic defects such as alpha-synuclein and parkin mutations in PD also underscores the important role of genetic factors in the disease. Thus, understanding the interplay between genes and environment in PD may be critical to unlocking the mysteries of this 200-year-old neurodegenerative disease. Pesticides and metals are the most common classes of environmental chemicals that promote dopaminergic degeneration. The organochlorine pesticide dieldrin has been found in human PD postmortem brain tissues, suggesting that this pesticide has potential to promote nigral cell death. Though dieldrin has been banned, humans continue to be exposed to the pesticide through contaminated dairy products and meats due to the persistent accumulation of the pesticide in the environment. This review summarizes various neurotoxic studies conducted in both cell culture and animals models following dieldrin exposure and discusses their relevance to key pathological mechanisms associated with nigral dopaminergic degeneration including oxidative stress, mitochondrial dysfunction, protein aggregation, and apoptosis.

Animals↗

The activities of drug-metabolizing enzymes in goats treated orally with the latex of Calotropis procera and the influence of dieldrin pretreatment.

The effects of oral administration of different doses of the latex of Calotropis procera on the activities of drug-metabolizing enzymes in the liver, kidneys and duodenal mucosa of Nubian goats were investigated. Lesions and changes in total plasma protein concentration and in the activities of plasma sorbitol dehydrogenase (SD), glutamate dehydrogenase (GD) and aspartate aminotransferase (AST) were studied. The daily oral administration of the latex at dose rates of 0.4 and 0.8 ml per kg for 7 days resulted in a significant inhibition of the activity of aniline 4-hydroxylase. No signfiicant effects on the activities of aminopyrine N-demethylase and UDP-glucuronyltransferase were observed. A single oral dose of 1.2 or 1.6 ml per kg killed goats within 7 h and resulted in increased activities of aminopyrine N-demethylase and aniline 4-hydroxylase. UDP-glucuronyltransferase was found to be insensitive to tissue injury induced by the latex of C. procera. There were no pathological changes in goats given 10 mg per kg of dieldrin alone or in those pretreated with dieldrin and given the latex at a dose rate of 1.2 ml per kg 14 days later. Dieldrin pretreatment resulted in the induction of the activities of drug-metabolizing enzymes in the liver, kidneys and duodenal mucosa and it may have protected goats from the lethal effects of the latex.

Administration, Oral↗

Toxicokinetic interactions and survival of Hyalella azteca exposed to binary mixtures of chlorpyrifos, dieldrin, and methyl mercury.

Chemical mixture interactions of chlorpyrifos, dieldrin, and methyl mercury were evaluated in Hyalella azteca. Survival of adult and juvenile organisms was evaluated following exposure to individual chemicals and in binary combinations. Binary interactions of the model chemicals on survival of adult and juvenile H. azteca were evaluated by concentration-response curve analysis as additive, synergistic, antagonistic, or independent. Chlorpyrifos and methyl mercury interacted additively, while dieldrin interacted independently with both chlorpyrifos and methyl mercury. Toxicodynamic interactions were evaluated by measuring accumulation and elimination of each model toxicant in the presence of a second toxicant. Chlorpyrifos significantly increased the amount of methyl mercury accumulated in the first 12 h of exposure. Dieldrin did not interact with chlorpyrifos or methyl mercury in the accumulation or elimination experiments. Accumulation of chlorpyrifos was not observed. Results of the current investigation demonstrate that chlorpyrifos and methyl mercury interact additively, which would otherwise be predicted to act independently.

Animals↗

In vitro disruption of ATP dependent active transport following treatment with aldrin and its epoxy analog dieldrin in a fresh water teleost, Labeo rohita.

Tissue homogenates of brain, gill, liver and kidney of Labeo rohita were subjected in vitro to the various concentrations as 5.00, 1.66, 0.55, 0.18 and 0.06 mu M of 2 organochlorine pesticides aldrin and dieldrin and the disruption of ATP dependent active transport (involving ATPase) was studied. The inhibition of total ATPase, Mg2+ and Na+, K+-dependent ATPase by both the pesticides was quite similar and there was an increased inhibition with increased concentration of the toxicant, however, at the lowest concentrations of both the pesticides stimulation was observed in all tissues except gill Mg2+ ATPase where insignificant inhibition was observed after dieldrin treatment. Inhibition of ATPase system was noted maximum in brain followed by gill, kidney and liver of the experimental fish, however in each tissue maximum inhibition of ATPase was noted after dieldrin treatment than that of th e aldrin treatment. Therefore, the observed action of these pesticides might be related to the ability of the compounds to alter the cellular membrane configuration by binding with the lipid portion of the membrane and this blocking the movement of substances by active transport.

Adenosine Triphosphatases↗