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Laboratory evaluation of fipronil, a phenylpyrazole insecticide, against adult Anopheles (Diptera: Culicidae) and investigation of its possible cross-resistance with dieldrin in Anopheles stephensi.

Adult mosquitoes from two strains of Anopheles gambiae and from three strains of Anopheles stephensi were exposed to 0.25% fipronil-treated papers in WHO test kits or to 500 mg fipronil m-2 impregnated mosquito netting in bioassay spheres. For comparison, tests were also carried out with the pyrethroid permethrin, using the same methods and doses, and on papers treated with 0.4 and 4% of the cyclodiene insecticide dieldrin. Compared with the same doses of permethrin, fipronil showed less and delayed activity. Two of the An stephensi strains were resistant to fipronil and dieldrin. To investigate whether this was due to a resistance mechanism in the An stephensi strains acting against both insecticides, the most fipronil- and dieldrin-tolerant strain was further selected in two separate lines with one of the insecticides, followed by tests with the insecticide that the line had not been selected with. This indicated a concomitant rise of resistance to dieldrin in the fipronil-selected line and vice versa. Repeated back-crossing of the two lines with a susceptible strain and re-selection with either dieldrin or fipronil gave evidence for the involvement of a single resistance mechanisms to both insecticides. Permethrin resistance in both lines declined with selection for dieldrin or fipronil and confirms the absence of cross-resistance between fipronil and pyrethroids.

Animals↗

Toxicity of dieldrin to bobwhite quail in relation to sex and reproductive status.

In a study of dieldrin toxicity to breeding and nonbreeding bob-white quail (Colinus virginianus), breeding birds of both sexes on long photoperiods were more susceptible to dieldrin poisoning than nonbreeding birds, although some differences were not statistically significant at the .10 level. Shortened photoperiods caused gonadal regression, weight loss, and additional mortalities among dieldrin-treated birds previously in breeding condition. Dieldrin did not influence food consumption, body weight, or egg production until about a week or less before death of individual birds. Dieldrin brain residues were higher among birds that died during the study than among survivors sacrificed at its termination. Among those that died, neither dieldrin treatment level, reproductive status, nor sex seemed related to brain residue levels. Nevertheless, within those factors, levels were slightly higher in the birds that died later in the test.

Animals↗

Suppression of MHV3 virus-activated macrophages by dieldrin.

Dieldrin (36 mg/kg body weight) administered intraperitoneally prolonged recovery from infection with mouse hepatitis virus 3 (MHV3) in the genetically-resistant A/J strain, affected the humoral anti-MHV3 IgG immune response, and inhibited the intrinsic antiviral activity of peritoneal macrophages upon in vitro rechallenge with the virus. Infection of untreated A/J animals and vehicle controls with MHV3 resulted in marked and reproducible activation of peritoneal macrophages, observed in vitro as resistance to MHV3-cytopathic effects 48 hr after rechallenge with the virus, whereas exposure to dieldrin resulted in apparent loss of the intrinsic capacity of cells to restrict replication of MHV3 and to protect them from cytolysis. In addition, in vitro treatment of MHV3 virus-activated macrophages with dieldrin, mitomycin C and X-irradiation, inhibited the intrinsic capacity of cells to restrict MHV3 replication. This mechanism of cellular restriction of the virus by MHV3-activated macrophages from the resistant A/J strain appeared to be one of the sensitive targets for the suppressive action of dieldrin on host resistance, as no major changes in macrophage cellular parameters were observed in in vitro studies of cell viability, adherence to plastic, and superoxide anion generation; the increased cell yield in the peritoneal exudates during MHV3 virus infection was not affected by dieldrin exposure; and the attachment and uptake of [3H]MHV3 by virus-activated macrophages was shown to be unchanged by dieldrin exposure.

Animals↗

A pesticide (dieldrin)-induced immunohemolytic anemia.

The unusual presentation of a factory worker with severe hemolytic anemia which remitted following splenectomy prompted a search for an environmental cause for red cell injury. The investigation showed the presence of an immunoglobulin in the patient's serum and on the red cells and small amounts of complement on red cells. The patient's serum caused agglutination of a normal person's red cells only when dieldrin-coated, a reaction blocked by first reacting the serum with dieldrin. The spleen of the patient had a greater than normal concentration of dieldrin, the source of dieldrin being dietary. It is concluded that dieldrin became immunogenic and provoked a chemical immunohemolytic anemia. The spleen played a major role in destruction of red cells injured by the immunopathic process and in accumulation of the antigenic substance dieldrin.

Anemia, Hemolytic↗

Transient inhibition of mixed lymphocyte reactivity by dieldrin in mice.

Dieldrin, a non-aromatic organochlorinated pesticide, was shown to be a potent modulator of the immune system. We had earlier demonstrated that mice treated with a single sublethal dose of dieldrin showed an impaired antibody response and reduced viral restriction mediated by macrophages. These dieldrin-induced immunosuppressive effects were shown to be dose dependent, when administered by the oral or intraperitoneal (i.p.) route. This study was undertaken to investigate the effect of dieldrin on the T-cell immune response. Lymphoid cells from mice injected i.p. 7 days earlier with 36 mg/kg body weight (0.6 LD50) dieldrin were assessed for their ability to recognize a foreign antigen and to proliferate in a mixed lymphocyte reaction (MLR) at 4, 7, 14 and 24 days post-treatment. We have demonstrated a strong but transient inhibition of MLR at 7 days after pesticide exposure. This effect was reversible and could not be attributed to a direct cell cytotoxicity, nor to the modulation of the T-cell ratio in lymphoid organs. Since the mitogen response was not impaired at this time point, we suggest that T-cell ability to recognize a foreign antigen can be altered by dieldrin, but not the proliferative potential of the cells.

Animals↗

Abrogation of graft-versus-host reaction by dieldrin in mice.

Sublethal exposure to the organochlorine pesticide, dieldrin, decreased the T-cell immune response in mice. Indeed, a transient inhibition of the mixed lymphocyte reactivity (MLR) was noted at 7 days after intraperitoneal exposure to 0.6 LD50 dieldrin. The present study was undertaken to further investigate the effects of dieldrin on the T-cell immune response, using the graft-versus-host reaction (GVHR) as a model, in order to assess T-cell subset efficiency. Lymphoid cells of A/J mice injected intraperitoneally 7 days earlier with 36 mg/kg body weight dieldrin were transferred into H-2-incompatible F1 hybrids. With this model, known to induce a marked GVHR, we have observed that dieldrin inhibited the potential of parental cells to induce a GVHR in hybrid mice. This effect could not be attributed to a direct cell cytotoxicity, nor to the modulation of major T-cell subsets as shown by thymic and peripheral T-cell subpopulation analysis. Collaboration processes between these cellular subsets seem to represent a potential site for the dieldrin-induced suppression.

Animals↗

Quantitative aspects of accelerated nuclear polyploidization and tumour formation in dieldrin treated CF-1 mouse liver.

Nuclear polyploidization in the livers of CF-1 mice, exposed to dieldrin (0, 1, 5 and 10 ppm in the diet), was studied up to the median time of liver tumour development (ranging from 15 to 27 months) in the respective treatment groups. In untreated controls nuclear polyploidization is characterized by a linear increase of octaploid nuclei with age. Approximately 4 months before tumour development a reduction in the tetraploid to diploid ratio is observed. Dieldrin treatment was found to enhance nuclear polyploidization in the initial phases of treatment, as expressed by a dose-dependent increase in octaploid nuclei. In 'steady-state' situations all age dependent changes in the level of polyploidization found in controls were also found in dieldrin treated mice. However, these changes occurred at an increasingly earlier age with higher dieldrin treatment levels. The decrease in the tetraploid:diploid ratio always takes place a few months before tumour development. This change in the ploidy level may thus be related to the subsequent liver tumour formation. The liver tumours themselves appear to originate from a diploid stem line, and were found to increase their degree of polyploidization during growth, eventually developing aneuploid nuclei. A comparison of nuclear polyploidization and liver tumour formation in CF-1 mouse liver for the given dietary dieldrin concentrations showed that liver tumour formation was associated with a constant level of polyploidization. Since polyploidization is an age-dependent process, these findings suggest that liver tumour formation is imminent at a constant biological age and that dieldrin may advance the biological age of CF-1 mouse liver.

Administration, Oral↗

Resistance to dieldrin + fipronil assorts with chromosome inversion 2La in the malaria vector Anopheles gambiae.

Cyclodiene insecticide resistance in malaria vector mosquitoes of the Anopheles gambiae species complex (Diptera: Culicidae) has been reported previously from several parts of Africa. We report resistance to dieldrin, a cyclodiene, in two laboratory strains of An. gambiae Giles sensu stricto code-named Ian P20 from Nigeria (1979) and CIG from Cote d'Ivoire (1997). Dieldrin resistance levels were high in adult female mosquitoes (40-75% survived exposure to 4% dieldrin for 1 h) and was closely linked with chromosomal paracentric inversion 2La. This inversion did not occur in Hardy-Weinberg proportions, but showed an excess of heterozygotes in both strains, which may account for the high levels of resistance. This linkage also suggests that dieldrin resistance in Ian P20 is dominant. After subsamples of strain Ian P20 were exposed for 1 h to dieldrin 4% or fipronil 2% (discriminating concentrations), the resultant mortality-rates (61% and 65%) were not significantly different. Most survivors after fipronil treatment also survived subsequent exposure to dieldrin (46/50=92%). This apparent cross-resistance between insecticides of two classes (cyclodiene and phenyl pyrazole) has implications for the management of insecticide resistance in wild populations of the An. gambiae complex.

Animals↗

The kinetics of nuclear polyploidization and tumour formation in livers of CF-1 mice exposed to dieldrin.

The kinetics of nuclear polyploidization in livers of CF-1 mice exposed to dieldrin were studied at concentrations of 0, 0.1, 1, 5 and 10 p.p.m. in the diet, in 'steady-state' situations (which are reached within a few weeks after initiation of treatment). Animals were killed at five time intervals (after 1.85, 3, 6, 9 and 14 months of exposure). The changes in the percentage of octaploid nuclei (8C) were used as an indicator of the kinetics of overall polyploidization. Polyploidization in control mice increased proportionally (linearly) with time (age). The enhancement of polyploidization by dieldrin was found to be proportional to dietary concentration. The slopes of the linear regressions of polyploidization, as a function of age, were identical in all dieldrin-treated groups and controls, indicating that there was no cumulative effect of dieldrin in time. A comparative analysis of the observed dieldrin dietary concentration: response relationship of polyploidization and of tumour formation in CF-1 mouse liver indicates that liver tumour formation is associated with a constant degree of polyploidization. Assuming that polyploidization reflects the ageing process, the data suggest that liver tumour formation is imminent at a constant biological age and that tumour promoters, such as dieldrin, could operate by advancing the biological age of mouse liver in the initial phases of treatment. The results of this study suggest that the analysis of ploidy changes may serve as an aid to perspective in evaluating risks associated with exposures to liver tumour promoters.

Aging↗

Effects of dieldrin on hepatic carbohydrate metabolism in the suckling and adult rat.

Hepatic carbohydrate metabolism was studied in adult and suckling rats given age-specific LD50 doses of dieldrin po. These doses in 5-, 10-, and 60-day-old Wistar rats were 38, 28, and 63 mg/kg, respectively. Plasma glucose and free fatty acids (FFA), and hepatic glycogen, phosphoenolpyruvate carboxykinase (PEPCK), fructose-1,6-diphosphatase (FDP), and glucose-6-phosphatase (G6P) were measured 1 and 3 h after administration of the insecticide. Plasma glucose concentrations were elevated (17%) in some 5-day-old rats after 1 h and in all adults after 1 and 3 h (45 and 30%, respectively). Plasma FFA concentrations were decreased (9%) in the 5-day-old rat 1 h after dieldrin. Hepatic glycogen content was reduced in both 5- and 10-day-old pups at 1 hour (22 and 17%, respectively). Hepatic FDP activity was elevated in the 5-day-old rat at 1 h (17%) and was decreased (10%) in the 10-day-old rat at 3 h. Hepatic PEPCK activity was increased in adult animals by 30% 1 h after dieldrin. Furthermore, PEPCK activity was increased at 3 h in rats of all ages (76%, 5-day-old pup; 115%, 10-day-old pup; 56%, 60-day-old adult). Hepatic G6P activity was unaltered by dieldrin. Thus only the activity of hepatic PEPCK is consistently elevated by dieldrin exposure. However, this enhanced PEPCK activity is associated with dieldrin-induced hyperglycemia only in the adult rat.

Aging↗

Dieldrin pollution of a human food chain.

1 An incident is described in which excessive mortality amongst a poultry flock alerted veterinarians. Investigation revealed dieldrin in the carcasses and in the wood litter used in the nesting boxes. 2 Because high levels of dieldrin were found also in eggs the Department of Community Medicine was alerted. 3 Those most at risk were the workers who could have absorbed dieldrin by inhalation and percutaneously, and by eating contaminated eggs. A number of other people were at risk having eaten contaminated eggs. 4 Twenty-one workers or members of their families were investigated by case histories and blood levels. They were all clinically well. The highest estimated daily intake of dieldrin in the diet was 3.8 mgm. The highest blood dieldrin level found was 0.016 microgram/ml. This intake was of the same order as the upper limit of no-toxic-effect of long-term daily dosage, but the blood level is well below the level at which symptoms may be expected. The fall in mean blood level over a year is consistent with a long half-life of dieldrin in the human. 5 The conflict of interest in conducting a comprehensive investigation and preventing undue public alarm is discussed, and how this was resolved in this episode is described.

Adolescent↗

Cancer mortality in workers exposed to dieldrin and aldrin: an update.

This study was conducted to investigate the possible long-term health effects, in particular carcinogenic effects, of occupational exposure to the organochlorine insecticides dieldrin and aldrin. We updated an earlier cohort mortality study of 570 employees involved in the production of these insecticides. All of the employees had worked in the production plants between 1 January 1954 and 1 January 1970 and were followed for cause-specific mortality until 1 January 2001. Based on dieldrin levels in blood samples taken during the exposure period, available for 343 workers, individual estimates of the total intake of dieldrin were estimated for all individual subjects in the cohort. The estimated total intake ranged from 11 to 7755 mg of dieldrin, with an average of 737 mg. One hundred and seventy-one workers had died before 1 January 2001, compared with an expected number of 226.6, giving a standardized mortality ratio (SMR) of 75.6 [95% confidence interval (CI): 64.6-87.7]. This deficit in total mortality was mainly attributable to a deficit in cardiovascular disease mortality, but cancer mortality was also lower than expected. The observed number of deaths from rectal cancer was significantly higher than expected (SMR = 300.0; 95% CI: 109.5-649.3), but was most pronounced in the low-intake subgroup and appears to be unrelated to exposure to dieldrin and aldrin. This study reinforces the earlier findings that occupational exposure of workers to significant amounts of dieldrin and aldrin has not led to a higher cancer mortality than would be found in an unexposed population.

Aldrin↗

Circadian rhythm changes in toxicity of the insecticide dieldrin on larvae of the migratory locust Locusta migratoria migratorioides.

Circadian changes in toxicity of the insecticide dieldrin were documented in the larvae (fifth stage) of the migratory locust, Locusta migratoria migratorioides. Insects were housed under light (L): dark (D) = 12:12, with L from 0800 to 2000 h. Topical applications of dieldrin at fixed clock hours, with doses ranging from 0.1 to 8 micrograms/gm body weight, were carried out in a series of experiments on male and female larvae. Twenty-four h after dosing, mortality was recorded to quantify the median lethal dose (LD50) values with reference to time of treatment. Experiments were performed during February, early and late June, and August. Larvae were more susceptible to dieldrin when dosed during the night rather than during the day [analysis of variance (ANOVA); p less than 0.05]. Moreover, female larvae were less susceptible to dieldrin than were male larvae (ANOVA; p less than 0.05). Cosinor analysis revealed circadian rhythms in susceptibility-resistance to the insecticide in all experiments except no. 2. Toxicity was found to be greatest during the nighttime. Cosinor analysis of pooled data of the four experiments documented circadian rhythmicity to toxicity of dieldrin in female but not in male larvae. Regardless of sex, the timing of least susceptibility (greatest resistance and highest LD50 value) to the insecticide, dieldrin, was around 1500.

Animals↗

Activation of human neutrophils in vitro and dieldrin-induced neutrophilic inflammation in vivo.

Many chemicals of environmental concern are known to alter the immune system and are considered toxic molecules because they affect immune cell functions. Inflammation related to environmental chemical exposure, however, is poorly documented, except that from air pollutants. In this study, we found that the organochlorine insecticide dieldrin could not alter the ability of human neutrophils to phagocytose opsonized sheep red blood cells at nonnecrotic concentrations (0.1, 1, 10, and 50 microM). However, dieldrin was found to increase human neutrophil superoxide production, RNA synthesis, and proinflammatory cytokine interleukin-8 production. The normal apoptotic rate of neutrophils evaluated by both cytology and flow cytometry (CD-16 staining) was not altered by dieldrin treatments, and this was correlated with its inability to inhibit spreading of neutrophils onto glass. Using the murine air pouch model, we found that dieldrin induces a neutrophilic inflammation. Taken together, these results demonstrated that dieldrin is a proinflammatory contaminant. To our knowledge, this is the first report establishing that dieldrin is a contaminant exhibiting proinflammatory properties. In addition, it is the first time that the murine air pouch model has been successfully used to confirm that a chemical of environmental concern can induce an inflammatory response in vivo.

Animals↗

Seasonal concentrations of dieldrin in water, channel catfish, and catfish-food organisms, Des Moines River, Iowa--1971-73.

Concentrations of dieldrin in aquatic insects, crayfish, minnows, and small carpsuckers, and muscle tissue of channel catfish (Ictalurus punctatus) were compared with the dieldrin content of Des Moines River water in 1971-73. Monthly mean concentrations of dieldrin in river water and most aquatic organisms were highest in June and July, soon after aldrin had been applied to corn land in the watershed. Several groups of aquatic organisms also exhibited high dieldrin levels in the fall when the dieldrin content of river water was seasonally low. The influence of temperature on metabolic rate and enzyme activity and the differences in body fat content were suggested as probable causes of variations observed in the dieldrin content of aquatic organisms.

Agriculture↗

Dieldrin resistance in Culex pipiens fatigans in Malaya.

Resistance to insecticides in Culex pipiens fatigans has already been reported from two areas in Malaya. In Penang two years' use of BHC as a larvicide resulted in the development of a strain which was found to have acquired a tenfold resistance to BHC, and also to dieldrin to which it had not been exposed. In Singapore, when larval control became unsatisfactory after 6 months' use of a dieldrin emulsion, laboratory experiments confirmed that active resistance to dieldrin had developed. The present observations report the finding of two further dieldrin-BHC resistant strains of C. p. fatigans in Malaya, but differ from the previous reports in that resistance, in one strain at least, was developed as a result of house-spraying with dieldrin against adult mosquitos. In this strain resistance to dieldrin was about 100 times in both adults and larvae, resistance to gamma-BHC in larvae was about 20 times, while resistance to DDT was slight.

Animals↗

Effects of dieldrin, diet, and bedding on enzyme function and tumor incidence in livers of male CF-1 mice.

The effects of naturally occurring microsomal enzyme inducers on hepatocellular drug-metabolizing enzyme systems and also upon the incidence of "spontaneous" liver tumors in CF-1 mice were investigated, using animals maintained on semisynthetic diet and filter-paper bedding as controls. The administration of dieldrin, a potent microsomal enzyme inducer with tumorigenic properties in livers of CF-1 mice, to some of the experimental treatment groups served as a positive control. Conventional diet and sawdust bedding caused induction of the liver monooxygenase system, although this effect was far less pronounced than that produced by dieldrin. The incidence of liver tumors in mice exposed to conventional diet and sawdust bedding was similar to that seen in the control group. The incidence of liver tumors was significantly increased in dieldrin-treated mice, including those maintained on semisynthetic diet and filter-paper bedding. Both benign and malignant tumors were found in dieldrin-treated mice, the latter type of lesion showing evidence of lung metastasis. These results, together with evidence that dieldrin and its mammalian metabolites possess neither genotoxic activity nor potential, are consistent with the concept that dieldrin exacerbates or facilitates the expression of a preexisting oncogenic factor which is genetically linked and possibly viral in origin.

Animals↗

Dieldrin and picrotoxinin modulation of GABA(A) receptor single channels.

The insecticide dieldrin is known to suppress the GABA(A) receptor-channel complex in a manner similar to that of picrotoxin. To elucidate the more detailed mechanisms of dieldrin and picrotoxin interactions with the GABA system, single-channel patch clamp experiments were performed using rat dorsal root ganglion neurons in primary culture. Dieldrin did not alter the open time distribution and mean current amplitude or the distribution of burst duration and the mean burst duration. However, the mean closed time was prolonged indicating that dieldrin decreased the channel open probability. Previous studies have demonstrated that dieldrin and picrotoxin share the common binding site on the GABA receptor. Thus, the effects of picrotoxinin on the GABA(A) receptor single channels were also examined. Dieldrin and picrotoxinin had similar effects at the single-channel level. These changes of single-channel parameters explain the suppressive effects of these chemicals on GABA-induced whole-cell currents.

Animals↗