Degradation of heptachlor epoxide and heptachlor by a mixed culture of soil microorganisms.
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Biotransformation↗
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Confirmation of pesticide residue identity. II. Derivative formation in solid matrix for the confirmation of DDT, DDD, methoxychlor, perthane, cis- and trans-chlordane, heptachlor, and heptachlor epoxide pesticide residues by gas chromatography.
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Chlordan↗
[Contributions on biological chemistry. XX. Distribution, excretion and metabolism of telodrin and heptachlor in rats and male rabbits, end product of heptachlor metabolism in warm blooded animals].
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Animals↗
Ecological toxicology and human health effects of heptachlor.
The chlorinated cyclodiene heptachlor was registered in 1952 as an agricultural and domestic insecticide. By early 1984, registration for all purposes, except subterranean termite control and for limited use in the control of fire ants, had been cancelled. This restriction of use arose primarily from concerns over the environmental persistance and bioaccumulation potential of the organochlorine pesticides. Currently, sale of heptachlor has been voluntarily suspended over questions about its carcinogenic potential, and the absence of safe and effective application methods. As a persistent organochlorine pesticide, heptachlor residues are detected in all components of the environment. In historical use, heptachlor was directly applied to terrestrial systems, while air and water were secondarily contaminated via volatilization and land run-off, respectively. Within each environmental compartment, heptachlor undergoes a variety of metabolic and abiotic transformations. In vivo studies indicate that heptachlor epoxide is the predominant metabolite, formed as a product of the mixed-function oxidase system, while 1-hydroxychlordene is the major soil metabolite. For quantification, heptachlor and its metabolites are extracted from air, soil and sediment, water, or biological materials using various organic solvents and analyzed by gas chromatography or thin-layer chromatography. Residue reports comprise most of the literature concerning the effects of heptachlor on the biota. In many such reports, toxic effects cannot be conclusively attributed to heptachlor exposure. Toxicity to organisms seems more dependent on acute exposure, while the chronic effects of low level exposure to heptachlor are poorly defined. Maximal terrestrial residues coincide with temporal and spatial proximity to application; peak residues in aquatic systems on the other hand, correlate to periods of maximum run-off. The lipophilic nature of both heptachlor and heptachlor epoxide results in the potential for significant bioaccumulation in all lipid-type compartments in the environment. The toxic effects of heptachlor are not specific for any one organ system. The liver and the central nervous system are most significantly affected by heptachlor, although effects can also be seen in the reproductive, hematopoietic, immune, and renal systems. An important consideration is the relation of relevant environmental exposure levels to toxicity. The concentrations necessary to elicit results in laboratory experiments do not translate directly to the same results upon environmental exposure, nor do experimental laboratory animal models absolutely equate with native-state organisms or with humans.(ABSTRACT TRUNCATED AT 400 WORDS)
Animals↗
Down-regulation of particulate protein kinase Cepsilon and up-regulation of nuclear activator protein-1 DNA binding in liver following in vivo exposure of B6C3F1 male mice to heptachlor epoxide.
The effects of in vivo administration of the cyclodiene tumor promoter heptachlor epoxide on mouse liver protein kinase C were studied in male B6C3F1 mice by protein kinase C activity assays and Western blotting under conditions known to increase the incidence of hepatocellular carcinoma because protein kinase C is thought to be critical in phorbol ester-induced tumor promotion. Under these test conditions, 20 ppm dietary heptachlor epoxide for 1-20 days increased cytosolic and decreased particulate total protein kinase C activities, while 10 ppm had no effect. Further, total cytosolic and particulate protein kinase C activities were decreased within 1 hour by 10 mg/kg intraperitoneal (i.p.) heptachlor epoxide. Western blotting showed that conventional protein kinase Calpha and beta isoforms were unaffected by heptachlor epoxide. Particulate novel protein kinase Cepsilon, however, was selectively down-regulated by 1, 10, and 20 ppm dietary heptachlor epoxide, whereas the cytosolic isoform was decreased by 1 and 10 ppm heptachlor epoxide for 10 days. The high-dose treatment for 24 hours also decreased particulate novel protein kinase Cepsilon but increased the cytosolic titer. These results demonstrate that this isoform is unique in its sensitivity to heptachlor epoxide. Activator protein-1 DNA binding, a critical factor in tumor promotion, was substantially increased at 3 and 6 hours with 3.7 mg/kg (i.p.) heptachlor epoxide and at 3 and 10 days with 20 ppm dietary heptachlor epoxide. The effects of heptachlor epoxide on protein kinase C and activator protein-1 are similar to those caused by phorbol ester treatments and correlate well to heptachlor levels found to induce tumors in mice. However, heptachlor epoxide did not initially activate protein kinase C with in vivo treatments or with in vitro treatments of a plasma membrane fraction aimed at demonstrating direct activation, as has been shown for phorbol esters. The ability of heptachlor epoxide to down-regulate particulate novel protein kinase Cepsilon correlates to dosages used in in vivo tumor promotion studies. However, this may represent a negative feedback response rather than a causative effect.
Animals↗
Heptachlor: uptake, depuration, retention, and metabolism by spot, Leiostomus xanthurus.
The estuarine fish, spot (Leiostomus xanthurus), was exposed to 0.27, 0.52, 1.01, 1.99, and 3.87 mug/liter technical grade heptachlor (65% heptachlor, 22% trans-chlordane, 2% cis-chlordane, 2% nonachlor, and 9% unidentified compounds) for 24 days in a flowthrough bioassay, followed by 28 days in heptachlor-free seawater. Concentrations of heptachlor, heptachlor epoxide, and trans- and cis-chlordane in edible tissues were monitored at day 3 and weekly thereafter throughout the bioassay and at the end of the postexposure period. All four chemicals were accumulated by spot. Maximum concentrations of heptachlor were observed on day 3; maximum concentrations of the other three compounds were observed on day 17. The average bioconcentration factors for heptachlor and trans-chlordane were 3,600 and 4,600, respectively. Only 10% or less of the maximum concentrations of heptachlor, heptachlor epoxide, and trans-chlordane accumulated during the exposure period remained after 28 days in pesticide-free seawater; an average of 35% of the cis-chlordane remained. Relative total amounts of heptachlor and cis-chlordane changed during the exposure and post-exposure periods. Nearly all of the heptachlor was eliminated or metabolized to its epoxide. Cis-chlordane, which averaged 4-7% of the total residues (chlordanes and heptachlors) in edible tissues during the exposure, increased to 18-23% of the total residues by the end of the postexposure period.
Animals↗
Effect of lindane and heptachlor on delta-aminolaevulinate synthase and its regulation.
The effect of lindane and heptachlor on haem metabolism was studied with the aim to elucidate the mechanism of their porphyrinogenic action. The effects of these compounds on delta-aminolaevulinate synthase (ALA-S) and ferrochelatase were evaluated and the mechanism of increase of ALA-S activity was especially studied. The results indicated the following: (1) Lindane and heptachlor produced increases in ALA-S activity; this effect was dependent on the drug dose, the time of treatment, and the development of the animal, the maximum response being obtained prior to hatching. Lindane was observed to have a greater effect on ALA-S than heptachlor. In fact, when effects of lindane and heptachlor were compared we observed that lindane produced: (a) greater increases in ALA-S activity (six fold vs four fold), both with respect to dimethyl sulphoxide (DMSO) controls (3.8+/-0.3 nmol ALA/g liver per h); (b) earlier ALA-S response (1.5 h vs 4 h); (c) responses at lower doses (0.3 mg/egg vs 1 mg/egg). (2) The increase in ALA-S activity produced by lindane or heptachlor is an induction and not an activation process since it depends on protein synthesis and the drugs per se have no effect. Thus, our results obtained from studies in ovo with actinomycin D and cycloheximide suggest that lindane is acting at the translational level while heptachlor interferes at the level of transcription. (3) The study of ALA-S subcellular distribution indicated no accumulation in the cytosol of DMSO controls and in the lindane or heptachlor treated embryos, neither of the chlorinated pesticides alter the normal subcellular distribution of this regulatory enzyme in the liver. (4) Exogenous haem was able to prevent or decrease the induction of ALA-S elicited by both pesticides, thus showing that lindane or heptachlor-induced ALA-S respond to haem regulation. (5) Lindane had no effect on ferrochelatase activity at the doses and times assayed, but heptachlor decreased this enzyme activity. The porphyrinogenic mechanism of lindane and heptachlor is discussed on the basis of the present results.
Animals↗
Possible mechanisms underlying the mitogenic action of heptachlor in rat hepatocytes.
The worldwide use of the organochlorine pesticide heptachlor has led to widespread contamination in the environment. Like many other organochlorine pesticides, heptachlor is considered to pose a threat to human health. It has been shown that heptachlor is a tumor-promoting agent, but the mechanisms involved still remain unclear. The negative response of heptachlor in in vitro genotoxicity test suggests that this pesticide displays its carcinogenicity through epigenetic pathways. With the growing evidence that proliferation accounts for the tumor-promoting effects of many agents, the purpose of this work was to investigate the mechanisms involved in the mitogenic activity of heptachlor in quiescent rat hepatocytes and to understand the properties of this compound as a tumor promoter in the liver. Heptachlor triggered significant proliferation in quiescent rat hepatocytes. Two mechanisms were delineated to support the mitogenic effect in the hepatocyte: activation of key kinases in signaling pathways and inhibition of apoptosis. Exposure to heptachlor led to activation of protein kinase C mitogenactivated protein kinases. Moreover, these results indicate that like many tumor promoters, heptachlor strongly inhibited TGFbeta-induced apoptosis and cytochrome c release into the cytosol. The levels of the anti-apoptotic protein Bcl-2 were also increased in the presence of heptachlor. In conclusion, these results indicate that heptachlor alters basic cell function by interfering with key cellular signaling pathways.
Animals↗
Neurotoxicity of the organochlorine insecticide heptachlor to murine striatal dopaminergic pathways.
Changes in biochemical status of nerve terminals in the corpus striatum, one of the primary brain regions affected in Parkinson's disease, were studied in groups of C57BL/6 mice treated by ip injection three times over a 2-week period with 3--100 mg/kg heptachlor. On average, the maximal rate of striatal dopamine uptake increased > 2-fold in mice treated at doses of 6 mg/kg heptachlor and 1.7-fold at 12 mg/kg heptachlor. Increases in maximal rate of striatal dopamine uptake were attributed to induction of the dopamine transporter (DAT) and a compensatory response to elevated synaptic levels of dopamine. Significant increase in V(max) of striatal DAT was not observed at doses > 12 mg/kg, which suggested that toxic effects of heptachlor epoxide may be responsible for loss of maximal dopamine uptake observed at higher doses of heptachlor. In support of this conclusion, polarigraphic measurements of basal synaptosomal respiration rates from mice treated with doses of heptachlor > 25 mg/kg indicated marked, dose-dependent depression of basal tissue respiration. At doses of 6 and 12 mg/kg heptachlor, which increased expression of striatal DAT, uptake of 5-hydroxytryptamine into cortical synaptosomes was unaffected. Thus, striatal dopaminergic nerve terminals were found to be differentially sensitive to heptachlor. This reduced sensitivity of serotonergic pathways was mirrored in the greater potency of heptachlor epoxide to cause release of dopamine from preloaded striatal synaptosomes in vitro compared to release of serotonin from cortical membranes. These results suggest that heptachlor, and perhaps other organochlorine insecticides, exert selective effects on striatal dopaminergic neurons and may play a role in the etiology of idiopathic Parkinson's disease.
Animals↗
Dopamine transporter binding in the rat striatum is increased by gestational, perinatal, and adolescent exposure to heptachlor.
Heptachlor is a persistent cyclodiene pesticide that affects GABAergic function. Recent reports indicate that heptachlor exposure also alters dopamine transporter (DAT) expression and function in adult mice. The aim of this study was to determine whether gestational, perinatal, and/or adolescent heptachlor exposure in rats altered dopamine-receptor and DAT binding. Adolescent exposure to dieldrin was included to evaluate the generality of the findings. Sprague-Dawley rats received doses (po) ranging from 0 to 8.4 mg/kg/day of heptachlor, or dieldrin, 3 mg/kg/day, during different developmental periods. There were dose-related decreases in maternal weight gain and pup survival, as well as delayed righting reflex, at heptachlor doses > or =3 mg/kg/day. There were no changes in striatal dopamine receptor-D1 ([(3)H]SCH-23390) and -D2 ([(3)H]spiperone) binding in preweanling pups exposed perinatally to heptachlor, and no differences in the response of adult rats to the motor activity-increasing effects of d-amphetamine. However, there were significant (27-64%) increases in striatal DAT binding of [(3)H]mazindol in preweanling rats exposed only gestationally. In rats exposed perinatally and/or during adolescence, there were also increases (34-65%) in striatal DAT binding at postnatal days (PND) 22, 43, and 128. Adolescent exposure to dieldrin also increased DAT binding. In other rats exposed perinatally and throughout adolescence, even the lowest dose of heptachlor 0.3 mg/kg/d increased DAT binding on PND 130. The DAT affinity for mazindol was unchanged in heptachlor-exposed striata. In vitro binding studies indicated that heptachlor (> or =10 microM) displaced mazindol binding. Thus, gestational, perinatal, and/or adolescent exposure to heptachlor produced an increase in DAT binding as early as PND 10, and this change persisted into adulthood.
Animals↗
Heptachlor: toxicity to and uptake by several estuarine organisms.
Technical-grade heptachlor (65% heptachlor, 22% trans-chlordane, 2% cis-chlordane, and 2% nonachlor) was tested in 96-hr bioassays to determine its toxicity to estuarine animals. The test organisms and the 96-hr LC50 or EC50s based on measured concentrations in water) are as follows: American oyster (Crassostrea virginica), 1.5 mug/liter; pink shrimp (Penaeus duorarum), 0.11 mug/liter; grass shrimp (Palaemonetes vulgaris), 1.06 mug/liter; sheepshead minnow (Cyprinodon variegatus), 3.68 mug/liter; pinfish (Lagodon rhomboides), 3.77 mug/liter; and spot (Leiostomus xanthurus), 0.85 mug/liter. Analytical-grade heptachlor (99.8% heptachlor) and heptachlor epoxide (99%) were also studied. The analytical-grade heptachlor 96-hr LC50 for pink shrimp and spot was 0.03 mug/liter and 0.86 mug/liter, respectively, while that for pink shrimp exposed to heptachlor epoxide was 0.04 mug/liter. Heptachlor was accumulated and some metabolized to its epoxide by all animals tested. Fish and oysters accumulated heptachlor in their tissues 2,800-21,300 times the measured concentration in water; shrimp, only 200-700 times.
Animals↗
Residues in cattle grazed on land contaminated with heptachlor.
Heptachlor epoxide residues exceeding the maximum residue limit of 0.2 mg/kg have been found in fat of cattle grazed on land previously treated with heptachlor prior to planting potatoes or maize. To determine the residues accumulated in cattle exposed to contaminated land and the rate of decline on removal from the contamination, steers were grazed on a former potato paddock which had been treated the 2 previous years with heptachlor at 1.1 kg/ha. Soil residues in the paddock varied from a total of 0.42 mg/kg heptachlor and its epoxide at the beginning of the trial to 0.31 mg/kg after 16 months. Residues in the soil decreased only slightly down to a depth of 300 mm. Pasture residues were less than 0.02 mg/kg (wet basis). Heptachlor epoxide residues in the body fat of the steers increased during 19 months of exposure and reached a maximum of 0.72 mg/kg. In 4 steers removed after 14 weeks exposure, the heptachlor epoxide concentrations continued to increase from a mean of 0.24 mg/kg to a mean of 0.34 mg/kg after a further 4 weeks. Concentrations then fell progressively with a half life of 11 weeks in the body fat. There was an apparent relationship between pasture length and body fat residue, with residues increasing as pasture length decreased. The results of the experiments preclude the option of grazing cattle on pasture grown on soil treated with heptachlor for any extended period of time. It is possible that if short pastures and soft soil are avoided, and if cattle are not exposed to contaminated land for any more than 1 week in each month, then residues would remain below the maximum residue limit of 0.2mg/kg heptachlor.
Adipose Tissue↗
Modulation of CPP32 activity and induction of apoptosis in Human CEM X 174 lymphocytes by heptachlor, a chlorinated hydrocarbon insecticide.
Heptachlor is an organochlorine insecticide used worldwide for the control of pests both agriculturally and domestically. Its lipophilic structure allows it to bioaccumulate and pass through the food chain, exposing those who come in contact with it to its tumor promoting and possible carcinogenic effects. As a mechanism of tumor promotion, we explored the possibility of heptachlor suppressing the apoptotic process in human CEM x 174 lymphocytes. In this article, we describe the effect of heptachlor on the activity of the apoptosis protease CPP32. We show that heptachlor by itself was able to stimulate CPP32 activity at relatively high concentrations. When combined with the chemotherapeutic agent doxorubicin, a known CPP32 activator, a dual effect was observed. Low concentrations of heptachlor (5 microM-10 microM) suppressed doxorubicin-induced CPP32 activity, and high concentrations of heptachlor (80 microM-120 microM) augmented it. We also showed that heptachlor alone at relatively high concentrations induced apoptosis-associated changes in CEM x 174 cells including high molecular weight (HMW) DNA cleavage and chromatin condensation. From these results, it appears that heptachlor has tumor promoting-like effects at lower concentrations, and at higher concentrations induces apoptosis as a mechanism of cytotoxicity.
Apoptosis↗
The organochlorine pesticide heptachlor disrupts the structure of model and cell membranes.
Heptachlor is an organochlorine pesticide which is particularly toxic for aquatic life. A significant source of this pesticide for infants is breast milk, where its concentration is considerably higher than in dairy milk. Given the lipophilic character of heptachlor, lipid-rich cell membranes are a very plausible target for its interaction with living organisms. In order to evaluate its toxicity towards cell membranes, heptachlor was made to interact with human erythrocytes and molecular models of the red cell membrane. These consisted of multilayers of dimyristoylphosphatidylcholine (DMPC) and dimyristoylphosphatidylethanolamine (DMPE), which are types of phospholipids that are respectively located in the outer and inner monolayers of the erythrocyte membrane, and large unilamellar vesicles (LUV) of DMPC. Observations by scanning electron microscopy showed that 10 mM heptachlor produced various degrees of shape alterations to erythrocytes, which ranged from a few blebs in some cells to a great number of protuberances in others. On the other hand, experiments performed by X-ray diffraction on DMPC and DMPE indicated that the bilayer structure of DMPC was much more affected by heptachlor than that of DMPE. Measurements by fluorescence spectroscopy on DMPC LUV confirmed the X-ray diffraction results in that both the hydrocarbon chain and polar head regions of DMPC were structurally perturbed by heptachlor. The results obtained from the model studies could explain the shape changes induced to red cells by heptachlor. According to the bilayer hypothesis, they were due to the preferential interaction of heptachlor with the phosphatidylcholine-rich external moiety of the erythrocyte membrane. It is therefore concluded that toxic effects of this pesticide can be related to its capacity to perturb the phospholipid bilayer structure, whose integrity is essential for cell membrane functions.
Dimyristoylphosphatidylcholine↗
Effect of heptachlor on hepatic mitochondrial oxidative phosphorylation in rat.
In a study of the hepatotoxicity of heptachlor (1,4,5,6,7,8,8-heptachlor 3a, 4,7,7 a-tetrahydro-4,7-methanoindene), a major compound of chlordane, the effect of heptachlor on the respiratory activity (oxidative phosphorylation and electron transport) of rat liver mitochondria was investigated. Heptachlor at a final concentration of 50 microM with succinate as substrate decreased the respiratory control index (RCI) due to a marked inhibition of state 3 respiration and a slight inhibition of state 4 respiration. One hundred microM heptachlor with succinate as substrate suppressed the states 3 and 4 respiration almost completely. On the other hand, heptachlor at a final concentration ranging from 50 to 100 microM with beta-hydroxybutylate (beta-HB) slightly decreased the RCI and decreased the RCI hardly at all with ascorbate plus N,N,N',N', -tetramethylphenylene diamine (TMPD) as substrate. Heptachlor at a concentration of 50 microM in the presence of succinate also decreased the ADP/O ratio of mitochondria. The mode of inhibition of succinate oxidation by heptachlor apparently is a noncompetitive inhibition, as shown by Lineweaver-Burk plot.
Animals↗
Elimination of [14C]heptachlor from body stores of lactating ewes treated with ovine growth hormone.
Elimination of [14C]heptachlor from body burdens of sheep was measured using mature ewes nursing single offspring, and the influence of exogenous ovine growth hormone (oGH) on elimination was studied. Six ewes (62 +/- 2.5 kg BW) were dosed (i.p.) once with [14C]heptachlor (2.04 mg/kg Bw; .88 microCi/mg heptachlor) and three were treated additionally with oGH (oGH; 5 mg/d) for 21 d. Three additional ewes served as controls. Excreta were collected each day for 21 d. Milk and blood were collected every 3rd d until ewes were euthanized at d 21. 14C activity was measured in excreta, milk, blood and tissues. Total cumulative activity of [14C]heptachlor and(or) metabolites in excreta (21 d) did not differ (P greater than .20) in ewes given oGH (25 +/- 2%) vs none (23 +/- 2%). Milk yield and protein content were unaffected (P greater than .10) by oGH. Ewes given oGH eliminated 2.2 +/- 2% of total 14C dosage into milk during 21 d, whereas ewes untreated with oGH eliminated 1.3 +/- .2% (P less than .10); total 14C activity eliminated into milk plus excreta was similar for ewes given oGH or none (P greater than .10). For all six ewes, half-times (T1/2) for distribution and elimination of 14C activity (heptachlor and metabolites) were 1.5 d and 11.7 d, respectively. Blood concentrations of 14C activity during 21 d yielded elimination half-time as 23 d. Unlike bovines, which eliminate heptachlor slowly (T1/2 approximately 70 to 80 d) and mainly into milk fat, lactating ovines eliminated heptachlor and(or) metabolites mainly into excreta and about sixfold faster than bovines.
Animals↗
Hepatic and muscle injuries in mice treated with heptachlor.
Heptachlor is a major component of the insecticide, chlordane. It is a health hazard but is still in use in some countries of Southeast Asia. To elucidate the toxicity of heptachlor its effects on mice after oral and intraperitoneal administration were studied. A 3-day group, 92-day group and 180-day group were given heptachlor intraperitoneally, orally and ad libitum, respectively. Results showed increased levels of serum alanine aminotransferase and decreased levels of serum cholinesterase activity. Serum creatine phosphokinase levels increased significantly. These may be due to the disruption of muscle membrane by chlordane. Results also showed significant variations of serum lipid levels from control as heptachlor has a known effect on lipid metabolism. Also the lipid peroxide levels expressed as TBA values were increased significantly, showing heptachlor's role in causing liver injury. These results suggest that the deterioration of membranes due to lipid peroxidation leads to liver and muscle injuries caused by heptachlor.
Alanine Transaminase↗
Heptachlor and the mitogen-activated protein kinase module in human lymphocytes.
The organochlorine pesticide heptachlor constitutes a potential health hazard because of its persistence in nature, its reported contamination in food and milk, and its possible carcinogenic effects. As a tumor promoter, heptachlor induces human myeloblastic leukemia cells to differentiate, and also down-regulates the tumor suppressor gene p53 in human immune cells. In this study, the heptachlor signaling pathway in human lymphocytes was studied. Addition of heptachlor to human CEM x174 lymphocytic cells reduced the cellular levels of MAP kinase (MAPK, mitogen-activated protein kinase) cascade proteins, including ERK1 (a 44-kDa MAPK), ERK2 (a 42-kDa MAPK), a 85-kDa and a 54-kDa MAP kinase, MEK1 (a 45-kDa ERK kinase) and MEKK (a 78-kDa MEK kinase). However, heptachlor treatment caused a marked increase in the expression of the activated (Thr- and Tyr-dually phosphorylated) ERK1 and ERK2 in the cells. These studies indicate that mitogen-activated protein kinases are important intermediates in the signal transduction pathway of immune cells upon heptachlor exposure, and the observation of stimulation of activated MAP kinases without a simultaneous accumulation of basal enzymes may suggest the involvement of a negative feedback control mechanism in the pathway.
B-Lymphocytes↗