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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↗

Rates of accumulation of dieldrin by a freshwater filter feeder: Sphaerium corneum.

The rate of dieldrin accumulation by Sphaerium corneum was determined in the field and under controlled conditions in the laboratory. The methods gave comparable results and it was established that Sphaerium attained an equilibrium concentration of dieldrin in its tissues in a short time period and exhibited a bioaccumulation factor of 1000. The rate of dieldrin accumulation by direct uptake from dieldrin in solution was compared to the rate obtained for indirect uptake from dieldrin adsorbed onto particulate material. The primary route of dieldrin uptake into Sphaerium was shown to be by direct partitioning of residues into lipoidal tissues from water. The effect of temperature on the rate of accumulation was also studied. The rate of accumulation increased with temperature in the range 5 degrees C to 20 degrees C. The frequency of gill cilia beat in relation to accumulation rate was studied in this temperature range and a correlation is shown.

Journal Article↗

Bioassays of aldrin and dieldrin for possible carcinogenicity.

Bioassays of technical-grade aldrin and dieldrin for possible carcinogenicity were conducted by administering the test materials in feed to Osborne-Mendel rats and B6C3F1 mice. Aldrin Groups of 50 rats of each sex were administered aldrin at one of two doses, either 30 or 60 ppm. Male rats were treated for 74 weeks, followed by 37-38 weeks of observation; female rats were treated for 80 weeks, followed by 32-33 weeks of observation. Matched controls consisted of groups of 10 untreated rats of each sex; pooled controls, used for statistical evaluation, consisted of the matched-control groups combined with 58 untreated males and 60 untreated females from similar bioassays of other chemicals. All surviving rats were killed at 111-113 weeks. Groups of 50 mice of each sex were administered aldrin at one of two doses for 80 weeks, then observed for 10-13 weeks. Time-weighted average doses were 4 or 8 ppm for males and 3 or 6 ppm for females. Matched controls consisted of groups of 20 untreated male mice and 10 female mice; pooled controls, used for statistical evaluation, consisted of the matched-control groups combined with 92 untreated male and 79 untreated female mice from similar bioassays of other chemicals. All surviving mice were killed at 90-93 weeks. Mean body weights attained by the rats and mice fed diets containing aldrin were similar to those of the controls during the first year of the study; however, mean body weights of the treated rats were lower than those of the controls during the second year of the study. Hyperexcitability was observed in all treated groups with increasing frequency and severity during the second year. Aldrin produced no significant effect on the mortality of rats or of male mice, but there was a dose-related trend in the mortality of female mice, primarily due to the early deaths in the high-dose groups. There was an increased combined incidence of follicular-cell adenoma and carcinoma of the thyroid both in male rats fed aldrin (matched controls 3/7, pooled controls 4/48, low-dose 14/38, high-dose 8/38) and female rats fed aldrin (matched controls 1/9, pooled controls 3/52, low-dose 10/39, high-dose 7/46). These incidences were significant in the low-dose but not in the high-dose groups both of males (P=0.001) and females (P=0.009) when compared with the pooled controls. Comparisons with matched controls, however, were not significant. Cortical adenoma of the adrenal gland was also observed in aldrin-treated rats in significant proportions (P=0.001) in low-dose (8/45) but not in high-dose (1/48) females when compared with pooled controls (0/55). Because these increased incidences were not consistently significant when compared with matched rather than pooled control groups, it is questionable whether the incidences of any of these adrenal tumors were associated with treatment. In male mice, there was a significant dose-related increase in the incidence of hepatocellular carcinomas (matched controls 3/20, pooled controls 17/92, low-dose 16/49, high-dose 25/45) when compared with either matched controls (P=0.001), or pooled controls (P<0.001). The incidence in the high-dose group was significant when compared with matched controls (P=0.002) or pooled controls (P<0.001). Dieldrin Groups of 50 rats and 50 mice of each sex were administered dieldrin at one of two doses. Low-dose rats and both low-and high-dose mice were treated for 80 weeks, followed by observation periods of 30-31 weeks for rats and 10-13 weeks for mice. Treatment of high-dose rats was terminated after 59 weeks and followed by 51-52 weeks of observation. Time-weighted average doses doses for rats were 29 or 65 ppm; doses for mice were 2.5 or 5 ppm. Matched controls consisted of groups of 10 untreated rats of each sex and 20 untreated male mice and 10 female mice; pooled controls, used for statistical evaluation, consisted of the matched-control groups combined with untreated animals from similar bioassays of other chemicals (58 male and 60 female rats, 92 male and 79 female mice). All surviving rats were killed at 110-111 weeks, and all surviving mice at 90-93 weeks. Mean body weights attained by the rats and mice fed diets containing dieldrin showed little or no differences compared with those of the controls during the first year of the study; however, mean body weights of the treated rats were lower than those of the controls during the second year of the study. Hyperexcitability was observed in all treated groups with increasing frequency during the second year, especially in high-dose rats. There was a marked increase in the mortality rate of rats during the first 90 weeks of the study. However, because of the high rates of mortality in the control groups during the remaining 20 weeks, survival could not be shown to be statistically dose responsive. In rats, there was a significant (P=0.007) difference between the combined incidence of adrenal cortical adenoma or carcinoma in the low-dose females (6/45) and that in the pooled controls (0/55). Although this tumor was also found in animals treated with aldrin, it is not clearly associated with treatment, because the incidence in the high-dose (2/40) was not significant, and the incidences were not significant when matched, rather than pooled, controls were used for comparison. In male mice, there was a significant positive dose-related trend (P=0.020) in the incidence of hepatocellular carcinomas using the pooled controls (pooled controls 17/92, low-dose 12/50, high-dose 16/45). When high-dose males were compared with the pooled controls, the results were also significant (P=0.025). It is concluded that under the conditions of these bioassays, none of the tumors occurring in Osborne-Mendel rats treated with aldrin or dieldrin could clearly be associated treatment. Aldrin was carcinogenic for the liver of male B6C3F1 mice producing hepatocellular carcinomas. With dieldrin, there was a significant increase in the incidence of hepatocellular carcinomas in the high-dose males which may be associated with treatment.

Journal Article↗

Equilibrium between uptake and elimination of dieldrin by channel catfish, Ictalurus punctatus.

Channel catfish, Ictalurus punctatus, measuring 150 (+/- 5)mm were exposed continuously to dieldrin for 70 days to determine if equilibrium between dieldrin uptake and elimination was reached by muscle tissue. Fish exposed to 13 parts per trillion (pptr) dieldrin reached equilibrium in 56 days, fish exposed to 27 pptr dieldrin were near equilibrium after 56 days, and fish exposed to 49 pptr dieldrin did not reach a balance between uptake and elimination after 70 days of exposure. Evidence of this study showed that balance between uptake and elimination was reached in less time at lower exposure levels than at higher levels.

Animals↗

The accumulation and loss of dieldrin and endrin in the eastern oyster.

Oysters demonstrated an ability to significantly concentrate dieldrin and endrin. Concentration ratios obtained after 168-hr exposures to endrin were 1670 at 0.1 mug/L and 2780 at 50 mug/L. Dieldrin was concentrated to higher levels. Exposure to 14C-labelled dieldrin at 0.5 mug/L produced whole body concentrations 2880 times the ambient level at 168 hr, while exposure to nine mug/L of dieldrin resulted in a concentration ratio of 2070 following the same period of exposure. Both endrin and dieldrin showed distinct linear regions in semi-logarithmic plots of uptake against time. Initial uptake was rapid and was followed by somewhat slower but still rapid uptake over the next 6 to 48 hr. Uptake within each of the stages followed an exponential form.

Animals↗

Dieldrin-14C elimination from turkeys.

A series of experiments were conducted to find ways of removing dieldrin2 residues from tissues of broiler-type turkeys (Meleagris gallopavo). The turkeys were contaminated with dieldrin and dieldrin-14C by oral dosing. Elimination was measured by assaying for 14C in the droppings. Carcass retention was measured by assaying the tissue for 14C, and in one experiment, dieldrin residues were measured by electron capture gas-liquid chromatography. Charcoal, Colestipol, and cholestyramine at dosages approximately equal to an intake of 5% of the diet were ineffective gastrointestinal adsorbants for removing dieldrin residues from the turkeys. Starvation accelerated the elimination of dieldrin from the turkeys, but only if the body lipids were reduced to approximately 10% or less of the carcass dry matter.

Aging↗

Induction of mixed function oxidases on oral administration of dieldrin.

The administration of dieldrin (30 mg/kg body weight) caused an increase in the liver weight of rats. The metabolism of aflatoxins B1 and G1 by the microsomes obtained from the liver of dieldrin-treated animals was enhanced significantly as compared to the controls showing that dieldrin increased the activity of mixed function hydroxylases. Dieldrin caused an increase in the activity of liver microsomal NADPH oxidase and a decrease in the lipid peroxidation. Dieldrin brought about an increase in the phosphatidylcholine content of rat liver.

Administration, Oral↗

Dieldrin inhibition of gap junctional intercellular communication in rat glial cells as measured by the fluorescence photobleaching and scrape loading/dye transfer assays.

Application of the fluorescence-recovery after photobleaching (FRAP analysis) technique and scrape loading/dye transfer assay was made to measure the presence of gap junctional communication in primary rat glial cells in vitro in the presence and absence of the neurotoxicant and tumor promoter dieldrin, a chlorinated insecticide. Results demonstrate that primary rat glial cells are able to exhibit gap junctional intercellular communication and that dieldrin at noncytotoxic concentrations can modulate gap junctional communication as early as 10 min after exposure to the chemical and that the effect is reversible after 4 hr recovery from the dieldrin exposure. Both the FRAP analysis and the scrape loading/dye transfer assay have validated the observation that dieldrin inhibits gap junctional communication in other cell types using different techniques to measure gap junction function. These results were interpreted as an indication that inhibition of gap junctional communication might contribute to the cellular mechanism of dieldrin's neurotoxicity.

Animals↗

Effect of dietary antioxidants on dieldrin-induced hepatotoxicity in mice.

An increasing number of reports suggest that oxidative stress plays a role in the toxicity of various xenobiotics, including organochlorine pesticides and drugs such as phenobarbital. Antioxidants appear to be protective against the damage induced by an acute dose of endrin, supporting the theory of a role for reactive oxygen in the toxicity of this class of compounds. The current study examined the effects of the dietary administration of vitamin C (400 mg/kg diet) or vitamin E (200 mg DL-alpha-tocopherol acetate/kg diet) on hepatotoxicity induced by subchronic (7 or 28 days) feeding of dieldrin (1, 3 and 10 mg/kg diet) to male B6C3F1 mice. Hepatoxicity induced by feeding of dieldrin for 28 days was evidenced by liver enlargement, hypertrophy of centrolobular hepatocytes, induction of hepatic ethoxyresorufin O-deethylase activity, and increased DNA synthesis in hepatocytes, particularly in centrolobular hepatocytes. Neither vitamin inhibited the dose-dependent increase in liver/body weight ratios, hypertrophy of centrolobular hepatocytes, or induction of hepatic ethoxyresorufin O-deethylase. Vitamin E, however, inhibited hepatic DNA synthesis at all dietary intakes of dieldrin, while vitamin C was inhibitory at 1 and 3, but stimulatory at 10 mg dieldrin per kg diet. The major changes in DNA labeling occurred in the centrolobular zones, but were not consistently inhibited by vitamins C or E. The ability of antioxidant vitamins to inhibit dieldrin-induced hepatic DNA synthesis suggests oxidative stress is involved in the toxicity of this compound; however, the inability of these vitamins to prevent all hepatotoxic changes indicates other factors are also involved.

Animals↗

Removal of dieldrin from aqueous solution by a novel triolein-embedded composite adsorbent.

In this study, a novel triolein-embedded activated carbon composite adsorbent (CA-T) was prepared and applied for the adsorption and removal of dieldrin from aqueous systems. Experiments were carried out to investigate the adsorption behavior of dieldrin on CA-T, including adsorption isotherms, adsorption kinetics, the influence of initial concentration, temperature, shaking speed, pH and the addition of humic acid (HA) on adsorption. The adsorption isotherms accorded with Freundlich equation. Three kinetics models, including pseudo-first-order, pseudo-second-order and intraparticle diffusion models, were used to fit the experimental data. By comparing the correlation coefficients, it was found that both pseudo-second-order and intraparticle diffusion models were used to well describe the adsorption of dieldrin on CA-T. The addition of HA had little effect on dieldrin adsorption by CA-T. Results indicated that CA-T appeared to be a promising adsorbent for removing lipophilic dieldrin in trace amount, which was advantageous over pure granular activated carbon (GAC). The adsorption rate increased with increasing shaking speed, initial concentration and temperature, and remained almost unchanged in the pH range of 4-8. Thermodynamic calculations indicated that the adsorption reaction was spontaneous with a high affinity and the adsorption was an endothermic reaction.

Adsorption↗

Dieldrin induces peroxisomal enzymes in fish (Sparus aurata) liver.

We have previously described the increase of microsomal lipid peroxidation and the appearance of new oxidized forms of Cu,Zn-superoxide dismutase in the liver of gilthead seabrams (Sparus aurata) injected with model xenobiotics, due to the increased production of reactive oxygen species (ROS) (Pedrajas et al., Chem. Biol. Interact., 1995). The effects of dieldrin and copper(II) on subcellular organelles directly related with ROS production are now studied. Immature fish were injected with dieldrin and copper, 0.15 and 1.0 mg/ kg, respectively. After 2 and 7 days, the livers were homogenized and the catalase and superoxide dismutase activities were determined in subcellular fractions isolated by differential centrifugation: nucleus, mitochondria, light mitochondrial fraction (LMF), microsomes and cytosolic fraction. Peroxisomes were isolated from LMF by discontinuous gradient centrifugation using Nycodenz. Changes in catalase and superoxide dismutase depended on the xenobiotic and affected to different subcellular fractions. Thus, the effects of copper(II) were mainly in nucleus and cytosol, whereas dieldrin induced catalase and superoxide dismutase (up to 2.8-fold) preferentially in nucleus and LMF fractions. Dieldrin-injected fish showed also highly increased activity of palmitoyl-CoA-oxidase (9.3-fold) and a nearly 2-fold increase in the protein concentration of the peroxisomal fraction. The results described above suggest that the oxidative stress previously detected for dieldrin in fish liver affects also to the peroxisomal enzymes.

Animals↗

Vitamin E modulation of dieldrin-induced hepatic focal lesion growth in mice.

The effect of vitamin E on dieldrin-induced hepatic focal lesion growth in male B6C3F1 mice previously treated with diethylnitrosamine (DEN) was investigated. After hepatic focal lesions were formed, mice were placed into one of the following treatment groups: Group 1, 50 mg vitamin E/kg diet (control NIH-07 diet); Group 2, 10 mg dieldrin/kg NIH-07 diet; Group 3, 10 mg dieldrin and 450 mg vitamin E/kg NIH-07 diet; and Group 4, 450 mg vitamin E/kg NIH-07 diet. Mice were killed and necropsied after 30 and 60 d of dietary treatment. The effect of treatment on lesion growth was examined by measuring the number of focal lesions per liver and the relative hepatic focal lesion volume. In addition, the possible cellular mechanism of focal hepatocyte growth was investigated by examining both focal DNA synthesis and apoptosis. Dieldrin treatment alone (Group 2) increased the focal lesion volume, focal lesion number, and focal lesion labeling index. Supplementation with vitamin E (Group 3) blocked this effect. Vitamin E supplementation to the diet alone (Group 4) also enhanced focal lesion growth and increased the number of lesions per liver, the relative focal volume, and the labeling index in hepatic focal lesions. Interestingly, vitamin E supplementation inhibited apoptosis in normal liver but did not produce an observable decrease in apoptosis in hepatic focal lesions. The present study showed that dieldrin (Group 2) or vitamin E supplementation alone (Group 4) promoted the growth of hepatic focal lesions in mice. However, when vitamin E is supplemented to dieldrin-fed mice (Group 3), there is an inhibition of hepatic focal lesion growth.

Animals↗