Responses of serum calcium and inorganic phosphate levels, parathyroid gland and C cells of Rattus norvegicus to heptachlor administration.

Intramuscular administration of two doses: 0.50 LD50 (14.70 mg/kg b w) and 0.75 LD50 (22.30 mg/kg b w) of heptachlor in Rattus norvegicus for 14 days induced significant hypocalcemia without altering serum inorganic phosphate value. Parathyroid chief cells of the experimental rats exhibited degranulation, vacuolation, loss of secretory granules and lipid droplets, reduction in chromatin, and degenerative changes in endoplasmic reticulum and cristae of the mitochondria. Not much of histological and ultrastructural changes could be seen in C cells of the heptachlor treated rats.

[The use amount of chlordane, heptachlor and heptachlor epoxide in Poland]. / Wielkosc spozycia chlordanu, heptachloru i epoksydu heptachloru w Polsce.

Chlordanes, heptachlor and heptachlor epoxide exposure from a particular food items in Poland in 1970-1996 was calculated by multiplying its annualized mean consumption rates by residue concentration in the food. Estimated daily dietary intakes of chlordanes were from 0.35 to 0.42 microgram per person while of heptachlor and heptachlor epoxide from 0.51 to 0.58 microgram per person, on the average. Fish, meat and meat products and butter are a main source of chlordanes intake in a total diet in Poland, while in the case of heptachlor and heptachlor epoxide a main source are meat, meat products and animal fats.

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.

The effects of perinatal/juvenile heptachlor exposure on adult immune and reproductive system function in rats.

This study was performed to determine if developmental exposure of rats to heptachlor (H) during the last half of gestation through puberty adversely affects adult functioning of the immune and reproductive systems. Time-bred pregnant female Sprague-Dawley rats were dosed by gavage with H (0, 30, 300, or 3000 microg/kg/day) from gestation day (GD) 12 to postnatal day (PND) 7, followed by direct dosing of the pups with H through PND 42. Separate groups of rats were evaluated with a battery of immune function tests, while other groups of rats were evaluated for reproductive development and function. Additional groups of rats were euthanized at the end of the dosing period for histological analyses of major organ systems. Some dams and PND 7 pups were euthanized; milk, plasma, fat and/or tissues were assayed for H and heptachlor epoxide B (HEB), a major metabolite of H. The amount of H and HEB found in milk, blood, fat, and tissues was proportional to the dose of H administered. There were no effects on the number or survival of pups born to H-exposed dams nor to pups exposed postnatally. There were no effects on the number of treated dams delivering litters or on litter size, nor were there any effects on any of the reproductive end points examined in the F(0) or F(1) rats. There were no effects of H exposure on lymphoid organ weights, splenic natural killer (NK) cell activity, and splenic lymphoproliferative (LP) responses to mitogens and allogeneic cells in a mixed lymphocyte response (MLR) assay at 8 weeks of age. H exposure did not alter delayed or contact hypersensitivity at 10 or 17 weeks of age, respectively. However, the primary IgM antibody response to sheep red blood cells (SRBCs) was suppressed in a dose-dependent manner in males, but not females, at 8 weeks of age. The percentage of B lymphocytes (OX12(+)OX19(-)) in spleen was also reduced in the high-dose males. The anti-SRBC IgM response was reduced only in males exposed to 30 microg H/kg/day in a separate group of rats 21 weeks of age. In these same rats, at 26 weeks of age, the secondary IgG antibody response to SRBCs was suppressed in all of the H-exposed males, but not females. These data indicate that perinatal exposure of male rats to H results in suppression of the primary IgM and secondary IgG anti-SRBC responses. Suppression of these antibody responses persisted for up to 20 weeks after the last exposure to H, at a total exposure of approximately 1500 microg H/kg/rat.

Heptachlor alters expression and function of dopamine transporters.

Epidemiological data support a relationship between pesticide exposure and Parkinson's disease; however, no experimental evidence has been provided to support this association. Here we report that subchronic administration of the organochlorine insecticide heptachlor (0, 3, 6, 9, or 12 mg/kg given 3 times over a 2 week period) leads to a pronounced increase in both the plasma membrane transport of dopamine and the expression of the plasma membrane dopamine transporter (DAT), as well as the vesicular monoamine transporter (VMAT2) in the striatum of C57BL mice. To address possible mechanisms of increased DAT and VMAT2 expression, we performed transport studies in cell lines expressing the human forms of either DAT or VMAT2. In a DAT expressing cell line, acute treatment with the putative toxic species of heptachlor, heptachlor epoxide, did not alter plasma membrane dopamine uptake. In a VMAT2 expressing cell line, heptachlor epoxide significantly inhibited vesicular uptake of dopamine (45% reduction at 10 microM). Since DAT has been proposed to be the molecular gateway for dopaminergic toxins, such as the parkinsonism-inducing neurotoxin MPP, and VMAT2 has been proposed to protect cells from MPP and other toxins by sequestering the toxin into vesicles, the combined effects of heptachlor could increase the susceptibility of the nigrostriatal dopamine system to neurodegeneration. We further propose that altered dopamine transport by exposure to pesticides may provide a molecular basis for the increased incidence of Parkinson's disease.

In vitro production of testosterone and plasma levels of luteinising hormone, testosterone and cortisol in male rats treated with heptachlor.

Male rats were divided into six groups of five rats each. Rats were injected subcutaneously with different concentrations of heptachlor for 2 weeks. Heptachlor at all doses significantly suppressed plasma testosterone levels (P < 0.05). Plasma luteinizing hormone (LH) (P < 0.01) and cortisol (P < 0.02) levels were significantly elevated in heptachlor-treated rats as compared to corn oil-treated controls. LH and testosterone levels showed strong correlation (r = 0.69, P < 0.05). The testes in rats treated with 25 mg/kg body weight of heptachlor showed some pathological changes. We conclude that heptachlor causes adverse effects on several male reproductive parameters in rats.

In vivo and in vitro effects of graded doses of the pesticide heptachlor on female sex steroid hormone production in rats.

Adult female Sprague-Dawley rats were injected with corn oil or 5 mg, 20 mg, 25 mg or 30 mg per kg body weight of heptachlor solution every other day for up to 18 days. The rats were killed at the end of the experimental period, and blood samples were assayed for progesterone and oestrogen by radioimmunoassay. Ovarian cells from the rats were isolated and incubated either on their own, or in the presence of LH or FSH, and production of progesterone and oestrogen determined. Control incubations consisted of cells from corn oil-treated rats. The latter were also incubated on their own or in the presence of LH or FSH. Heptachlor significantly suppressed blood progesterone and oestradiol levels (P < 0.05 to P < 0.001), the degree of suppression depending on the dose and the stage of the oestrous cycle in which samples were obtained. Production of oestradiol by ovarian cells from heptachlor-treated rats was lower than for corn oil-treated controls. Cells from rats treated with low doses of heptachlor (5 mg per kg body weight) showed an increased production of progesterone, while high doses (> 20 mg per kg body weight) suppressed production.

Effects of graded doses of the pesticide heptachlor on body weight, mating success, oestrous cycle, gestation length and litter size in laboratory rats.

Adult female Sprague-Dawley rats were injected with 5 or 20 mg/kg body weight heptachlor solution every other day for up to 18 days. They were weighed every day and the stage of oestrus determined by vaginal smears. One experimental group was mated and pregnancy characteristics studied. Heptachlor affected body weights, cycle patterns, length of gestation period and litter sizes in a dose-related manner. At a dose of 20 mg/kg body weight, heptachlor caused a significant decrease in average body weight (P < 0.01), disrupted and/or prolonged oestrous cycles, decreased mating success (P < 0.001), slightly increased gestation length (P < 0.05) and decreased litter size (P < 0.01).

The reproductive effects of dietary heptachlor in mink (Mustela vison).

Adult female mink were fed diets containing 0 (control), 6.25, 12.5, and 25 ppm (micrograms/g) technical grade heptachlor prior to and throughout the reproductive period (181 days) to evaluate the effects of heptachlor consumption on reproduction and offspring viability and to assess the extent of placental and mammary transfer of heptachlor epoxide to mink offspring. Feeding 12.5 and 25 ppm resulted in significant reductions in feed consumption and body weights of female mink. Mortality was 0, 8, 67, and 100% for the control, 6.25, 12.5, and 25 ppm groups, respectively. All females in the 25 ppm group died within 88 days. Mink fed the two higher heptachlor diets displayed clinical signs indicative of central nervous system involvement just prior to death. Females were mated with males on the same dietary treatments. Whelping success rates were 67, 83, 27, and 0% for the control, 6.25, 12.5, and 25 ppm groups, respectively. High mortality in the 12.5 and 25 ppm groups accounted for the lack of reproductive success. Gestation length, litter size and birth weight of kits were not significantly affected by adult female consumption of 6.25 ppm heptachlor while kits helped by females on the 12.5 ppm diet weighed significantly less than control kits at birth. Survival of kits in the 12.5 ppm group from birth to three weeks of age was also adversely affected. At three and six weeks of age, kit body weights in both the 6.25 and 12.5 ppm groups were significantly less than body weights in control kits.(ABSTRACT TRUNCATED AT 250 WORDS)

Exposure of applicators and residents to chlordane and heptachlor when used for subterranean termite control.

Research was conducted to assess dermal and respiratory exposure to applicators from chlordane and heptachlor used for subterranean termite control and exposure to residents of treated homes. Dermal exposure of 29 applicators was evaluated by using gauze pads attached to outer and inner clothing at selected body regions. Respiratory exposure of applicators was monitored with personnel-type air samplers worn during application periods. Air samplers were equipped with polyurethane foam plugs to trap airborne chlordane and heptachlor. Exposure of residents was measured by sampling ambient air of 19 homes treated with the termiticides. Electric air samplers equipped with foam plugs were used to monitor ambient air from the basement, the kitchen, and one bedroom at: 24 h prior to termiticide application, during application, and post-application at 24 h, 1 wk, and monthly for 6 mo. Applicator dermal exposure was estimated based on exposure rates to each body region. Respiratory exposure was estimated based on termiticide concentrations in the air and on the ventilation rate of a person doing light work. Residents' exposure was estimated based on the amount of termiticide present in ambient air. Results indicated that applicator exposure rates to chlordane and heptachlor were 2.54 and 1.88 micrograms/kg/h, respectively. Residents were exposed to less than 0.69 and 2.86 micrograms/m3 of chlordane and heptachlor, respectively. During this research, the application of termiticide containing chlordane and heptachlor posed minimal risk in terms of acute exposure to either the applicators or the residents of the treated homes.

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.

Gliosarcoma with chromosome abnormalities in a neonate exposed to heptachlor.

A neonate with a cerebral gliosarcoma was found to have chromosome abnormalities in tissue culture of the tumor, but normal karyotyping of peripheral blood. Similarities to and differences from chromosome abnormalities found in other human gliomas are noted. Unusual exposure of the child to heptachlor during prenatal development and the neonatal period suggests the need for further studies on the role of toxins in oncogenesis.

[Thymus changes in chicks following treatment with small doses of insecticides]. / Thymusveränderungen bei Kücken nach Behandlung mit kleinen Insektiziddosen

Effects of small doses of insecticides (Fenclorfos and Heptaclor) upon the thymus of chickens were followed. Treatment began at the age of 3 weeks and continued during 4 or 8 weeks. Doses used were: 1 ppm for Heptaclor and 1 ppm and 0.5 ppm for Fenclorfos. Total nucleic acid, total protein, RNA, DNA, and amino acid nitrogen contents were determined, as well as GOT and GPT activities and weight of the organ. Results are interpreted as being due to the action of insecticides on the hypothalamus-hypophysis-adrenals axis. They depend on the nature and dosis of insecticide, as well as on the duration of the treatment.