Chlorinated insecticides (toxaphene and endrin) affect oxytocin, testosterone, oestradiol and prostaglandin secretion from ovarian and uterine cells as well as myometrial contractions in cow in vitro.

We examined the direct effects of toxaphene and endrin, chlorinated insecticides that are widespread in the environment, on myometrial contractions and on the secretion of hormones involved in regulating these contractions. Granulosa, luteal, endometrial and myometrial cells, and myometrial strips from non-pregnant cows were incubated with both insecticides at environmentally relevant doses. Toxaphene inhibited and endrin stimulated the secretion of testosterone and oestradiol from granulosa cells. Toxaphene also inhibited and endrin stimulated the expression of the mRNA encoding the precursor of oxytocin (OT), as well OT secretion in luteal cell cultures. Moreover, endrin increased OT secretion from granulosa cells. Neither insecticide exerted an effect on progesterone secretion from luteal cells. Only toxaphene decreased the secretion of prostaglandins (PGF2 and PGE2) from endometrial cells. Meanwhile, only endrin decreased basal myometrial contractions, which was accompanied by inhibition of PGF2 secretion from the myometrium. Both endrin and toxaphene also decreased the force of the OT-stimulated myometrial contractions, whereas only toxaphene inhibited the stimulatory effect of OT on the force of myometrial contractions. In contrast to endrin, toxaphene decreased synthesis and secretion of one of the primary stimulators of myometrial contractions (OT) and indirectly inhibited OT signal reception in the myometrium by reducing E2 secretion. Both insecticides decreased OT-stimulated myometrial contractions; therefore, they may inhibit further transmission of the OT signal. Moreover, endrin inhibited basal myometrial contractions, potentially resulting from reduced PGF2 secretion from the myometrium. Our data indicate the potential of these insecticides to disturb the course of the oestrous cycle or fertilisation.

Comparative effects of TCDD, endrin, naphthalene and chromium (VI) on oxidative stress and tissue damage in the liver and brain tissues of mice.

The mechanism of toxicity of structurally diverse environmental toxicants including heavy metals and polyhalogenated and polycyclic hydrocarbons may involve a common cascade of events which entails an oxidative stress and production of reactive oxygen species. We have determined the comparative effects of single 0.01, 0.10 and 0.50 LD(50) doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), endrin, naphthalene and sodium dichromate (chromium VI) on lipid peroxidation, DNA fragmentation and enhanced production of superoxide anion (cytochrome c reduction) in liver and brain tissues of C57BL/6NTac mice. The effects of a single acute oral 0.50 LD(50) dose of these xenobiotics on hepatic and brain lipid peroxidation were investigated at 0, 12, 24, 48, and 96 h after treatment, while the effects of 0.10 LD(50) and 0.01 LD(50) doses of these xenobiotics were at 0, 24, 48, 72, and 96 h after treatment. Dose- and time-dependent effects were observed with all four xenobiotics. At a 0.50 LD(50) dose of TCDD, endrin, naphthalene and chromium VI, maximum increases in cytochrome c reduction (superoxide anion production) of approximately 5.7-, 5.4-, 5.3- and 4.1-fold, respectively, were observed in hepatic tissues. TCDD showed an increasing effect through 96 h. Endrin and naphthalene demonstrated a maximum effect at 12-24 h, while chromium VI exhibited a maximum effect at 48 h. With respect to lipid peroxidation, at a 0.50 LD(50) dose both endrin and chromium VI induced the maximum effect at 48 h of treatment, while naphthalene demonstrated the maximum effect after 24 h of treatment. TCDD demonstrated a continued effect through 96 h of treatment. At a 0.50 LD(50) dose TCDD, endrin, naphthalene and chromium VI produced maximum increases in hepatic lipid peroxidation of approximately 3.5-, 3.1-, 3.7- and 3.3-fold in hepatic tissues, respectively. Similar results were obtained in hepatic and brain DNA fragmentation at 0.50 LD(50) doses. Lesser effects were observed with 0.10 and 0.01 LD(50) doses of these xenobiotics as compared to the 0.50 LD(50) dose. The results clearly demonstrate that these diverse xenobiotics induce dose- and time-dependent oxidative stress and tissue damage in the liver and brain tissues of mice.

Role of p53 tumor suppressor gene in the toxicity of TCDD, endrin, naphthalene, and chromium (VI) in liver and brain tissues of mice.

It has been postulated that tumor suppressor genes are involved in the cascade of events leading to the toxicity of diverse xenobiotics. Therefore, we have assessed the comparative effects of 0.01, 0.10, and 0.50 median lethal doses (LD(50)) of 2,3,7, 8-tetrachlorodibenzo-p-dioxin (TCDD), endrin, naphthalene, and sodium dichromate (VI) [Cr(VI)] on lipid peroxidation, DNA fragmentation, and enhanced production of superoxide anion (cytochrome c reduction) in liver and brain tissues of p53-deficient and standard C57BL/6NTac mice to determine the role of p53 gene in the toxic manifestations produced by these diverse xenobiotics. In general, p53-deficient mice are more susceptible to all four xenobiotics than C57BL/6NTac mice, with dose-dependent effects being observed. Specifically, at a 0.50 LD(50) dose, naphthalene and Cr(VI) induced the greatest toxicity in the liver tissue of mice, and naphthalene and endrin exhibited the greatest effect in the brain tissue. At this dose, TCDD, endrin, naphthalene, and Cr(VI) induced 2.3- to 3.7-fold higher increases in hepatic lipid peroxidation and 1.8- to 3.0-fold higher increases in brain lipid peroxidation in p53-deficient mice than in C57BL/6NTac mice. At a 0. 10 LD(50) dose, TCDD, endrin, naphthalene, and Cr(VI) induced 1.3- to 1.8-fold higher increases in hepatic lipid peroxidation and 1.4- to 1.9-fold higher increases in brain lipid peroxidation in p53-deficient mice than in C57BL/6NTac mice. Similar results were observed with respect to DNA fragmentation and cytochrome c reduction (superoxide anion production). For example, at the 0.10 LD(50) dose, the four xenobiotics induced increases of 1.6- to 3. 0-fold and 1.5- to 2.1-fold in brain and liver DNA fragmentation, respectively, and increases of 1.5- to 2.3-fold and 1.4- to 2.5-fold in brain and liver cytochrome c reduction (superoxide anion production), respectively, in p53-deficient mice compared with control C57BL/6NTac mice. These results suggest that the p53 tumor suppressor gene may play a role in the toxicity of structurally diverse xenobiotics.

TCDD, endrin and lindane induced oxidative stress in fetal and placental tissues of C57BL/6J and DBA/2J mice.

The abilities of TCDD, endrin and lindane to induce oxidative stress in fetal and placental tissues have been studied after the oral administration of these xenobiotics to pregnant C57BL/6J and DBA/2J mice. Production of superoxide anion, lipid peroxidation and DNA-single strand breaks (SSB) was determined in live fetal and placental tissues 48 hr after administration of single teratogenic doses of the compounds on day 12 of gestation. Oxidative stress and its biomarkers were also determined in livers of day 18 fetuses after administration on day 12 of gestation. TCDD given at doses of 30 and 60 micrograms/kg body weight to the C57BL/6J and DBA/2J mice, respectively, produced increases of 1.3-2.7-fold in superoxide anion production, 1.6-1.9-fold in lipid peroxidation and 2.1-4.4-fold in DNA-SSB. Endrin, given at a dose of 4.5 mg/kg body weight to C57BL/6J and DBA/2J mice, produced increases of 1.3-2.8-fold in superoxide production, 1.4-1.8-fold in lipid peroxidation and 1.4-4.7-fold in DNA-SSB. Lindane when given at a dose of 30 mg/kg body weight to C57BL/6J and DBA/2J mice produced increases of 1.6-3.0-fold in superoxide production, 1.3-2.1-fold in lipid peroxidation and 1.4-5.0-fold in DNA-SSB. The results suggest that superoxide production, lipid peroxidation and DNA-SSB in fetal and placental tissues may participate in the fetotoxic effects of TCDD and other polyhalogenated cyclic hydrocarbons, and that TCDD-induced oxidative damage in fetal and placental tissues is mediated at least in part by the Ah-receptor. The results also indicate that TCDD as an inducer of oxidative tissue damage in the embryos and placentas is approximately 150 and 1000 times more potent than endrin and lindane, respectively, in C57BL/6J mice, and 75 and 500 times more potent than endrin and lindane, respectively, in the DBA/2J mouse strain.

In vitro and in vivo induction of heat shock (stress) protein (Hsp) gene expression by selected pesticides.

The chloroacetamide insecticide alachlor, polyhalogenated cyclic hydrocarbons endrin and chlordane and the organophosphate pesticides chlorpyrifos and fenthion induce oxidative tissue damaging effects including lipid peroxidation and nuclear DNA-single strand breaks. The mechanism involved in the induction of oxidative stress by these xenobiotics is unknown. No information is available regarding whether these pesticides can induce the expression of heat shock (stress) protein (Hsp) genes as a common protective mechanism against tissue damage. The pesticides were administered p.o. individually to female Sprague-Dawley rats in two 0.25 LD50 doses at 0 h and 21 h. The animals were killed at 24 h, and liver, brain, heart and lung tissues were removed to examine the induction of Hsps by Western and Northern blot analysis. In a separate series of experiments, cultured neuroactive PC-12 cells were treated 24 h with 50, 100 or 200 nM concentrations of these pesticides. Alachlor, endrin, chlorpyrifos and fenthion induced Hsp89 alpha and Hsp89 beta in hepatic and brain tissues, as well as in cultured PC-12 cells. Chlordane induced some expression of Hsp89 alpha but not Hsp89 beta in the hepatic and brain tissues of treated rats. Some expression of Hsp89 beta was observed in lung tissues of endrin and alachlor treated animals. These findings were substantiated by Western blot analysis using Hsp90 antibody. Except chlordane all these pesticides induced enhanced synthesis of Hsp90 in cultured PC-12 cells. The results indicate striking tissue differences in the patterns of the Hsps induced by the pesticides which were used, and demonstrate that these pesticides can induce the expression of Hsp89 alpha and Hsp89 beta genes in various target organs of rats. The results support the hypothesis that these genes may be mechanistically involved in protecting tissues against oxidative stress induced by structurally diverse pesticides.

Comparative teratological studies on TCDD, endrin and lindane in C57BL/6J and DBA/2J mice.

The teratogenic effects of endrin and lindane have been determined and compared to those induced by TCDD in the fetuses of C57BL/6J and DBA/2J mice after the administration of single oral doses to pregnant mice on day 12 of gestation. TCDD produced dose-dependent decreases in fetal weight, fetal thymic weight and placental weight, and dose-dependent increases in fetolethality, cleft palate formation and hydronephrosis at doses of 10-30 and 30-60 micrograms/kg body weight in C57BL/6J and DBA/2J mice, respectively. No maternal death was observed at the given doses in both strains of mice. Endrin (4.5 and 6 mg/kg body weight) and lindane (30 and 45 mg/kg body weight) produced significant decreases in fetal weight and placental weight in C57BL/6J and DBA/2J mice, and dose-dependent decreases in fetal thymic weight in C57BL/6J mice but not DBA/2J mice. Endrin and lindane caused 0-25 and 14-25% maternal deaths, respectively, at the above mentioned doses. Neither cleft plate nor hydronephrosis were induced by endrin or lindane in the two strains of mice. The results support the hypothesis that TCDD-induced cleft plate and hydronephrosis involve mechanisms that are Ah (aryl hydrocarbon) receptor mediated. However, other fetotoxic effects induced by TCDD, and the fetotoxic effects induced by endrin and lindane may involve additional unknown mechanisms that are not related to the Ah-receptor.

In vitro and in vivo generation of reactive oxygen species, DNA damage and lactate dehydrogenase leakage by selected pesticides.

Reactive oxygen species may be involved in the toxicity of various pesticides and we have, therefore, examined the in vivo effects of structurally dissimilar polyhalogenated cyclic hydrocarbons (PCH), such as endrin and chlordane, chlorinated acetamide herbicides (CAH), such as alachlor, and organophosphate pesticides (OPS), such as chlorpyrifos and fenthion, on the production of hepatic and brain lipid peroxidation and DNA-single strand breaks (SSB), two indices of oxidative stress and oxidative tissue damage. The selected pesticides were administered p.o. to female Sprague-Dawley rats in two 0.25 LD50 doses at 0 h and 21 h and killed at 24 h. In a parallel set of experiments, we have determined the in vitro effects of these pesticides on the DNA-SSB and enhanced lactate dehydrogenase leakage (LDH) from neuroactive PC-12 cells in culture. In vitro production of reactive oxygen species by these pesticides was also assessed by determining the enhanced chemiluminescence responses of hepatic and brain homogenates. Following treatment of rats with endrin, chlordane, alachlor, chlorpyrifos and fenthion, increases of 2.8-, 3.0-, 4.2-, 4.3- and 4.8-fold were observed in hepatic lipid peroxidation, respectively, while at these same doses, increases in lipid peroxidation of 2.4-, 2.1-, 3.6-, 4.6- and 5.3-fold, respectively, were observed in brain homogenates. Increases of 4.4-, 3.9-, 1.6-, 3.0- and 3.5-fold were observed in hepatic DNA-SSB following treatment of the rats with endrin, chlordane, alachlor, chlorpyrifos and fenthion, respectively, while at these same doses, increases of 1.9-, 1.7-, 2.2-, 1.4-, 1.4-fold, respectively, were observed in brain nuclear DNA-SSB. Following in vitro incubation of hepatic and brain tissues with 1 nmol/ml of each of the five pesticides, maximum increases in chemiluminescence occurred within 4-7 min of incubation and persisted for over 10 min. Increases of 3.0-, 2.7-, 3.6-, 4.9- and 4.4-fold were observed in chemiluminescence following in vitro incubation of the liver homogenates with endrin, chlordane, alachlor, chlorpyrifos and fenthion, respectively, while increases of 1.7-, 1.8-, 2.0-, 3.4- and 3.7-fold, respectively, were observed in the brain homogenates. Increases of 2.2-, 2.3-, 2.9-, 2.9- and 3.4-fold were observed in the chemiluminescence responses in the liver homogenates of the animals treated with endrin, chlordane, alachlor, chlorpyrifos and fenthion, respectively, while increases of 1.8-, 2.0-, 3.2-, 2.9- and 2.4-fold, respectively, were observed in the brain homogenates. Cultured neuroactive PC-12 cells were incubated with the pesticides and the release of the enzyme lactate dehydrogenase (LDH) into the media as an indicator of cellular damage and cytotoxicity was examined. Maximal release of LDH from cultured PC-12 cells was observed at 100 nM concentrations of the pesticides. Increases of 2.3-, 2.5-, 2.8-, 3.1 and 3.4-fold were observed in LDH leakage following incubation of the PC-12 cells with endrin, chlordane, alachlor, chlorpyrifos and fenthion, respectively. Following incubation of the cultured PC-12 cells with 100 nM concentrations of these same pesticides, increases in DNA-SSB of 2.5-, 2.2-, 2.1-, 2.4- and 2.5-fold, respectively, were observed. The results clearly demonstrate that these different classes of pesticides induce production of reactive oxygen species and oxidative tissue damage which may contribute to the toxic manifestations of these xenobiotics. Reactive oxygen species may serve as common mediators of programmed cell death (apoptosis) in response to many toxicants and pathological conditions.

Predicting ecotoxicological impacts of environmental contaminants on terrestrial small mammals.

This review examines whether the effects of environmental contaminants on wild small mammals can be predicted from the results of single-species, laboratory toxicity studies. Heavy metals, organochlorines, chlorinated aromatic hydrocarbons, and OP/carbamate pesticides were identified as the groups of xenobiotics for which there are toxicity data for terrestrial small mammals and that, on the basis of persistence, acute toxicity, and bio-accumulation potential, present the greatest hazard to wild mammals. Laboratory-generated toxicity data, which used lethality and reproduction as measurable endpoints, were reviewed and intake and residue LOAELs estimated for representative chemicals (lead, endrin, PCBs) from the heavy metal, organochlorine, and chlorinated aromatic hydrocarbon substance groups; the OPs and carbamates were reviewed as a whole. Intakes and residues of these compounds in wild small mammals were compared with laboratory-defined LOAELs and the likelihood of effects predicted. The accuracy of these predictions was examined and the efficacy of extrapolating toxicity data from laboratory to wild species assessed. Qualitative extrapolation from laboratory to wild species was good for all the chemicals considered, laboratory tests correctly identifying the types of effects chemicals had on a wide range of wild mammals. In contrast, the quantitative extrapolation of dose-response data was either poor or largely unvalidated. This is because interspecies variation in sensitivity to xenobiotics and the effects on toxicity of differences in exposure pattern between laboratory and wild species are largely unquantified. Based upon the limited evidence available, errors in the direct extrapolation of dose-response data from laboratory to field may be as large as three orders of magnitude. Direct extrapolation of residue-response data from laboratory to wild mammals is good both for the effects of heavy metals on specific organs and for residues and acetylcholinesterase inhibition associated with pesticide-induced mortality. The use of organ residues or biomarkers to predict the severity of sublethal effects on reproductive output may be possible, although large residues or biomarker responses are not necessarily indicative of the severity of wider physiological effect. Appropriate residues/biomarkers may differ for various xenobiotics and even between species for the same xenobiotic. Further research is required to identify suitable markers that can be correlated with the occurrence and magnitude of ecologically important effects. Xenobiotics likely to have a direct effect on population dynamics are those that are persistent and adversely affect survival and reproduction. At present, this weak correlation is the only one that can be made between single-species laboratory tests and population effects.(ABSTRACT TRUNCATED AT 400 WORDS)

Comparative effects of endrin on hepatic lipid peroxidation and DNA damage, and nitric oxide production by peritoneal macrophages from C57BL/6J and DBA/2 mice.

1. Endrin is a polyhalogenated cyclic hydrocarbon which produces hepatic and neurologic toxicity. In order to further assess the mechanism of toxicity of endrin, the dose-dependent effects of endrin on hepatic lipid peroxidation and DNA damage, and nitric oxide (NO) production by peritoneal exudate cells (primarily macrophages) were investigated in C57BL/6J and DBA/2 mice which vary at the Ah receptor genetic locus. C57BL/6J mice are dioxin-responsive, while DBA/2 mice are dioxin-insensitive. 2. Mice of both strains were treated with 0, 1, 2 or 4 mg endrin kg-1 as a single oral dose in corn oil, and the animals were killed 24 hr post-treatment. At doses of 1, 2 and 4 mg endrin kg-1 in C57BL/6J mice, hepatic mitochondrial lipid peroxidation increased 1.2-, 2.2- and 3.2-fold, respectively, and 1.8-, 2.3- and 3.5-fold with microsomes, respectively. At these same doses in DBA/2 mice, hepatic mitochondrial lipid peroxidation increased 1.3-, 2.0- and 2.6-fold, respectively, and 1.5-, 1.9- and 2.5-fold with microsomes, respectively. 3. Increases of 2.3-, 2.4- and 4.9-fold were observed in hepatic DNA damage (elution constants) in C57BL/6J mice at doses of 1, 2 and 4 mg endrin kg-1, respectively, while at these same three doses, increases of 1.9-, 2.1- and 2.3-fold were observed for DBA/2 mice, respectively.(ABSTRACT TRUNCATED AT 250 WORDS)

Comparative studies on lipid peroxidation and DNA-single strand breaks induced by lindane, DDT, chlordane and endrin in rats.

1. A variety of structurally dissimilar polyhalogenated cyclic hydrocarbons produce similar toxic effects. The molecular mechanisms involved in the production of these toxic manifestations is not known. 2. We have proposed that reactive oxygen species may be involved, and have therefore examined the time-dependent effects of lindane (30 mg/kg), DDT (40 mg/kg), chlordane (120 mg/kg), and endrin (4.5 mg/kg) on the production of hepatic mitochondrial and microsomal lipid peroxidation and DNA single strand breaks, two indices of oxidative stress. 3. All four xenobiotics resulted in significant increases in hepatic lipid peroxidation and DNA damage. Earliest (6 hr) increases in both lipid peroxidation and DNA damage were observed following lindane administration. Time-dependent increases in both parameters were observed following endrin administration. 4. Maximum increases in DNA single strand breaks of 2.8- and 2.5-fold were observed 12 hr after DDT and chlordane administration, respectively, while a 4.4-fold increase was observed 24 hr after endrin administration. 5. The results demonstrate that the four structurally dissimilar polyhalogenated hydrocarbons produce oxidative tissue damage which may contribute to the toxic manifestations of these xenobiotics, and exhibit different toxicokinetic properties.

In vitro induction of reactive oxygen species by 2,3,7,8-tetrachlorodibenzo-p-dioxin, endrin, and lindane in rat peritoneal macrophages, and hepatic mitochondria and microsomes.

Hepatic mitochondria and microsomes as well as peritoneal macrophages from female Sprague-Dawley rats were incubated for up to 30 min at 37 degrees C in the presence of 0-200 ng/ml 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), endrin (1,2,3,4,10,10-hexachloro-6,7-epoxy-1,4,4 alpha,5,6,7,8,8 alpha-octahydroendo, endo-1,4:5,8-dimethanonaphthalene), and lindane (hexachlorocyclohexane). Production of reactive oxygen species was determined by chemiluminescence and cytochrome c reduction, while potential tissue damage was assessed by alterations in membrane fluidity. Chemiluminescence, a sensitive but nonspecific measure of free radical generation, increased 40-70% when macrophages (3 x 10(6) cells/ml), mitochondria and microsomes (1 mg/ml) were incubated with the three polyhalogenated cyclic hydrocarbons (PCH). Maximum increases in chemiluminescence occurred within 5-10 min of incubation and persisted for over 30 min. The cytochrome c reduction assay is most specific for superoxide anion production. When hepatic mitochondria were incubated with endrin and lindane for 15 min at 100 ng/ml, increases in cytochrome c reduction of 6.5- and 7.5-fold occurred, respectively, while when microsomes were incubated with these same two PCH, increases in cytochrome c reduction of 8.6- and 11.6-fold occurred, respectively. When mitochondria, microsomes, and macrophages were incubated with TCDD under identical conditions, small increases in superoxide anion production were detected. Changes in microsomal membrane fluidity were determined spectrofluorometrically following incubation with the three PCH using diphenyl-1,3,5-hexatriene as the fluorescent probe. TCDD, endrin, and lindane enhanced microsomal membrane apparent microviscosity by 2.3-, 2.1-, and 2.5-fold, respectively, indicating a significant decrease in membrane fluidity.(ABSTRACT TRUNCATED AT 250 WORDS)

Sodium and GABA-activated channels as the targets of pyrethroids and cyclodienes.

The symptoms of poisoning by the pyrethroid and cyclodiene insecticides are characterized by hyperexcitation and convulsions followed by paralysis. The main target site of the pyrethroids has been identified to be the sodium channels which are kept open for unusually long periods of time, causing a prolonged sodium current to flow which, in turn, leads to hyperexcitation of the nervous system. We have now found large differential sensitivity to the pyrethroids in two types of sodium channels. The dorsal root ganglion neurons of the rat were endowed with two types of sodium channels, one sensitive to the blocking action of tetrodotoxin (TTX) and the other insensitive to TTX. The type I pyrethroid allethrin and the type II pyrethroid deltamethrin were both effective in prolonging the sodium current in the TXX-resistant sodium channel but had only a small effect on the TTX-sensitive sodium channel. These two types of sodium channels also exhibited marked differences in their physiological properties, including the time course of current, the activation voltage, and the steady-state inactivation. In contrast to the pyrethroids, lindane and the cyclodienes endrin, isobenzan, dieldrin and heptachlor-epoxide suppressed the GABA-induced chloride current. The initial transient component of the chloride current was blocked more than the late sustained component. The suppression of the GABA-mediated synaptic inhibition would cause hyperexcitation of the nervous system. The results are compatible with the convulsant action of these insecticides.

Endrin-induced urinary excretion of formaldehyde, acetaldehyde, malondialdehyde and acetone in rats.

Previous studies have shown that endrin induces an oxidative stress in rats as demonstrated by an increase in hepatic lipid peroxidation, a decrease in glutathione content and a decrease in the activity in selenium-dependent glutathione peroxidase. We have therefore examined the effects of orally administering 1.5, 3.0, 4.5 and 6.0 mg endrin/kg on the urinary excretion of the lipid metabolites formaldehyde, malondialdehyde, acetaldehyde and acetone. The simultaneous determination of these four lipid metabolites may be a useful biomarker for assessing exposure to xenobiotics which induce an oxidative stress and enhanced lipid peroxidation. Urine samples were collected up to 72 h post-treatment. The identities of the lipid metabolites were confirmed by gas chromatography-mass spectroscopy, while the 2,4-dinitrophenylhydrazine derivatives of these metabolic products were quantitated by high pressure liquid chromatography. Maximum increases in the excretion of the four lipid metabolites occurred at approx. 24 h post-treatment at all doses with no significant increases in excretion occurring thereafter. The maximum increases in excretion of malondialdehyde, formaldehyde, acetaldehyde and acetone were approx. 160%, 93%, 121% and 162%, respectively, relative to control values. Seventy-two hours after endrin administration, the liver weight/body weight and spleen weight/body weight ratios significantly increased while the thymus weight/body weight ratio markedly decreased. The results demonstrate that endrin induces dose- and time-dependent alterations in lipid metabolism with the enhanced excretion of specific metabolic products in the urine.

Endrin-induced increases in hepatic lipid peroxidation, membrane microviscosity, and DNA damage in rats.

Endrin is a polyhalogenated cyclic hydrocarbon pesticide which produces hepatic and neurologic toxicity. Previous studies have indicated that endrin induces hepatic lipid peroxidation. In order to further assess the possible role of lipid peroxidation in the toxicity of endrin, the dose- and time-dependent effects of endrin on hepatic lipid peroxidation, membrane microviscosity and DNA damage in rats were examined. Rats were treated with 0, 3.0, 4.5, or 6.0 mg endrin/kg as a single oral dose in corn oil, and the animals were killed 0, 12, 24, 48, or 72 h post-treatment. Dose-dependent increases in hepatic mitochondrial and microsomal lipid peroxidation and microviscosity as well as nuclear DNA single strand breaks were observed as early as 12 h post-treatment. Maximum increases in these three parameters occurred 24 h after endrin administration at all three doses. While the incidence in DNA damage decreased with time after 24 h, the incidence of lipid peroxidation and microviscosity of microsomal and mitochondrial membranes remained relatively constant. Dose- and time-dependent increases in liver and spleen weight/body weight ratios with decreases in thymus weight/body weight ratios were observed. The data indicate that endrin administration induces hepatic lipid peroxidation which may be responsible for the increased membrane microviscosity as a result of membrane damage as well as enhanced DNA damage.

Excretion of formaldehyde, malondialdehyde, acetaldehyde and acetone in the urine of rats in response to 2,3,7,8-tetrachlorodibenzo-p-dioxin, paraquat, endrin and carbon tetrachloride.

Formaldehyde (FA), acetaldehyde (ACT), malondialdehyde (MDA) and acetone (ACON) were simultaneously identified in urine, and their excretion quantitated in response to chemically induced oxidative stress. Urine samples of female Sprague-Dawley rats were collected over dry ice and derivatized with 2,4-dinitrophenylhydrazine. The hydrazones of the four lipid metabolic products were quantitated by high-performance liquid chromatography on a Waters 10-microns mu-Bondapak C18 column. The identities of FA, ACT, MDA and ACON in urine were confirmed by gas chromatography-mass spectrometry. An oxidative stress was induced by orally administering 100 micrograms/kg 2,3,7,8-tetrachlorodibenzo-p-dioxin, 75 mg/kg paraquat, 6 mg/kg endrin or 2.5 ml/kg carbon tetrachloride to rats. Urinary excretion of FA, ACT, MDA and ACON increased relative to control animals 24 h after treatment with all xenobiotics. The system has wide-spread applicability to the investigation of altered lipid metabolism in disease states and exposure to environmental pollutants.

Intrinsic lethality of chloride-channel-directed insecticides and convulsants in mammals.

The intrinsic lethality of a series of chloride-channel-directed convulsants and insecticides was determined by intracerebral injection into mice. The toxicities of the cyclodiene insecticides and picrotoxinin were potentiated by intracerebral injection, when compared to their reported intraperitoneal LD50s. In contrast, the toxicities of lindane, abamectin, and the bicyclic convulsants TBPS and a TBOB analog were approximately the same by either route of administration. These results suggest that the brain is the primary target site for the cyclodienes and picrotoxinin, while the peripheral nervous system may be relatively more important in the toxic action of lindane, abamectin, and bicyclic convulsants such as TBPS. With the exception of picrotoxinin these compounds showed, overall, a good correlation between acute intracerebral toxicity and potency for inhibiting GABA-dependent chloride uptake. The evidence that multiple chloride-channel subtypes serve as targets for these compounds and the potential impact this had on the results of these studies are discussed.

Effect of endrin on the hepatic distribution of iron and calcium in female Sprague-Dawley rats.

The distribution of iron and calcium in hepatic subcellular fractions of female rats treated with endrin (1,2,3,4,10,10-hexachloro-6,7-epoxy-1,4,4 alpha,5,6,7,8,8 alpha- octahydroendo,endo-1,4:5,8-dimethanonaphthalene) was determined. Endrin in corn oil was administered orally to rats in single doses of 3, 4.5, or 6 mg/kg, and the animals were killed at 0, 12, 24, 48, or 72 hr post-treatment. Iron and calcium were determined by atomic absorption spectroscopy. The administration of endrin increased the iron content of mitochondria and decreased the iron content of microsomes and nuclei. Significant increases occurred in the calcium content of mitochondria, microsomes, and nuclei. Thus, the results indicate that with respect to the subcellular distribution of iron and calcium, endrin produces differential effects. Vitamin E succinate administration partially prevented the endrin-induced hepatic alterations in iron and calcium homeostasis. Endrin also produced dose- and time-dependent increases in the liver and spleen weight/body weight ratios, while decreasing the thymus weight/body weight ratios. The altered distribution of calcium and iron may contribute to the broad range of effects of endrin.