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PubMedDate not supplied

Organochlorine pesticide residue levels in human milk: Western Australia, 1979-1980.

Two hundred sixty-seven samples of breast milk, supplied by 140 donors from both urban (N = 45) and rural (N = 95) areas, were analyzed on a whole milk basis for aldrin, gamma-benzene hexachloride (gamma BHC), hexachlorobenzene (HCB), dieldrin, and total dichlorodiphenyltrichloroethane (DDT) to ascertain the effectiveness of restrictions placed on pesticide use since 1971. Aldrin and gamma BHC were found to be present mainly in trace amounts, while decreases were found with HCB (0.025-0.008 ppm) and total DDT (0.078-0.046 ppm). Dieldrin showed an increase (0.005-0.009 ppm) which caused some concern. The results of a questionnaire suggested a connection between the high dieldrin levels and a program of treatment for the protection of houses against termites. A statistical analysis further supported this theory and suggested three variables being significantly associated with dieldrin levels: (1) treatment of the house, (2) suburb in which the donor lived, and (3) age of the mother. Further relationships were shown to exist between pesticide levels, lipid content of the milk, and the stage of feeding at which the sample was taken.

Analysis of Variance↗
PubMed2002

Human health significance of organochlorine and mercury contaminants in Japanese whale meat.

The concentrations of total mercury, polychlorinated biphenyls (PCBs), and organochlorine pesticides (SigmaDDT, dieldrin, hexachlorobenzene [HCB], and SigmaHCH) were determined in 61 whale meat products (bacon, blubber, red meat, liver, intestine, and tongue) purchased from retail outlets across Japan. Mean (range) concentrations of contaminants in all samples were: total mercury 4.17 (0.01-204); SigmaPCB 1.14 (0-8.94); SigmaDDT 0.98 (0-7.46); dieldrin 0.07 (0-0.35); HCB 0.06 (0-0.22); and SigmaHCH 0.07 (0-0.19) micro g/g (wet weight). The data were used to calculate estimated daily intakes (EDIs) of contaminants at two hypothetical levels of whale meat consumption. These EDIs were compared with FAO/WHO "tolerable daily intake" (TDI) values for each chemical. EDIs calculated for higher levels of whale meat consumption were in some cases exceptionally high and for many products exceeded FAO/ WHO-TDIs for total mercury, PCBs, and dieldrin, with exceedance factor values (EDI/TDI) for total mercury, PCBs, and dieldrin reaching maxima of 175, 5.36, and 2.1, respectively. For sensitive consumers and those with high-level consumption (e.g., whaling communities), exposure to mercury and to a lesser extent PCBs from certain whale blubber and bacon and striped dolphin liver products could lead to chronic health effects. The Japanese community should therefore exercise a precautionary approach to the consumption of such foods in excess, particularly by high-risk members of the population.

Animals↗
PubMed1987

Central nervous system toxicity of some common environmental residues in the mouse.

To ascertain changes in the level of general central nervous system (CNS) excitability and, therefore, postulated neurotoxicity of some common environmental residues, a bioassay was developed that used a known general CNS stimulant, pentylenetetrazol (PTZ, Metrazol). As a positive control, dieldrin was compared to PTZ and nine other compounds (caffeine, 1,2,3-trichloropropane, ethylene dibromide, Arochlor 1254, pentachlorophenol, heptachlor epoxide, DDT, lindane, and chlordecone) for CNS stimulatory effects, both acutely and subchronically. All doses were administered on an equimole per kilogram basis, rather than milligram per kilogram or %LD50 comparisons. The general level of CNS excitability elicited by each compound relative to the others was assessed. Of the 10 compounds examined, dieldrin showed the most activity in decreasing metrazol-challenge ED50, while chlordecone was most potent in increasing the ED50. Dieldrin, heptachlor epoxide, and chlordecone were shown to potently inhibit PTZ-induced kindling. Of all compounds examined, dieldrin is concluded to have the greatest potential for causing an increase in general CNS excitability, which may relate to persistent behavioral stimulation.

Animals↗
PubMedDate not supplied

Serum levels of several organochlorine pesticides in farmers correspond with dietary exposure and local use history.

In response to reported increased cancer risks among farmers, the Agricultural Health Study (AHS) was designed to examine health outcomes and environmental exposures among farm families in the United States. In the pilot phase of the AHS, food, beverage, air, dermal, dust, surface wipe, and biological specimens (blood and urine) were collected and analyzed for six farm families in two states (IA and NC). In addition, questionnaires were administered to examine previous pesticide use. This paper reports the organochlorine pesticide results of the serum and dietary analyses as well as questionnaire results from the pilot exposure study of farmers and their families. Note, no organochlorine pesticides were reported as currently being applied to the study farms. In all human serum samples examined, typical U.S. population levels were found for the majority of the pesticides. In addition, human serum levels of organochlorine pesticides showed no significant daily or seasonal variation. However, serum trans-nonachlor levels were found to be higher in people living on the two farms in North Carolina than in people living on the four farms in Iowa (p < 0.05). Further, unusually high dieldrin levels were found in serum samples from a farmer and spouse living on an Iowa farm, and these levels were significantly higher than those of people living on the other farms (p < 0.05). Dieldrin was persistent in the foods consumed on the same Iowa farm where family members showed elevated serum levels. In addition, dietary samples from the North Carolina farms exhibited high levels of chlordane. No organochlorine pesticides were found in any of the drinking water samples. Dietary dieldrin levels on the same Iowa farm exceeded the oral reference dose (RfD) eight- to eleven-fold (50 ng/kg-day). No other pesticide exceeded the RfD. However, dietary chlordane levels at a North Carolina farm reached 17% of the RfD. Previous use of aldrin on an Iowa farm corresponded to dieldrin found in the diet and in the serum of the farmer and spouse. Previous reported use of chlordane on the North Carolina farms corresponded with measurable dietary levels of chlordance and higher serum trans-nonachlor levels than the levels in Iowa farm families.

Adult↗
PubMed1985

A case of fatal endrin poisoning.

Ingestion of 12 g of endrin by a 49-year-old man caused convulsions persisting for 4 days, hypersalivation, hyperthermia, renal insufficiency, thrombocytopenia and recurrent hypotension. Death followed after 11 days, due to pulmonary complications (infection and haemorrhage) and hypoxaemia causing bradycardia and cardiac arrest. Endrin and dieldrin concentrations in blood 4 hours, 6 and 11 days after ingestion were respectively 450, 86 and 71 micrograms/l for endrin and 60, 19 and 19 micrograms/l for dieldrin. Dieldrin was also present, possibly because the endrin preparation contained traces of dieldrin. Endrin concentrations 11 days after ingestion were 0.071 mg/l in blood, in adipose tissue 89.5 mg/kg, in the heart 0.87 mg/kg, in the brain 0.89 mg/kg, in the kidneys 0.55 mg/kg and in the liver 1.32 mg/kg.

Endrin↗
PubMed1996

Dietary exposures to selected metals and pesticides.

Average daily dietary exposures to 11 contaminants were estimated for approximately 120,000 U.S. adults by combining data on annual diet, as measured by a food frequency questionnaire, with contaminant residue data for table-ready foods that were collected as part of the annual U.S. Food and Drug Administration Total Diet Study. The contaminants included in the analysis were four heavy metals (arsenic, cadmium, lead, mercury), three organophosphate pesticides (chlorpyrifos, diazinon, malathion), and four organochlorine pesticides (dieldrin, p,p'-DDE, lindane, heptachlor epoxide). Dietary exposures to these contaminants were highly variable among individuals, spanning two to three orders of magnitude. Intraindividual exposures to the metals, organophosphates, and organochlorines were estimated to be strongly correlated; Pearson's correlation coefficients ranged from 0.28 for lindane:dieldrin to 0.84 for lead:mercury. For some of the compounds (e.g., arsenic and dieldrin), a substantial fraction of the population was estimated to have dietary intakes in excess of health-based standards established by the EPA. Before use for risk assessment or epidemiologic purposes, however, the validity of the exposure estimates must be evaluated by comparison with biological indicators of chronic exposure. Because of their low detection rate in table-ready foods, the estimated distributions of exposures for dieldrin, p,p'-DDE, heptachlor epoxide, lindane, diazinon, and chlorpyrifos were found to be sensitive to assumed values for nondetect samples. Reliable estimates of the population distribution of dietary exposures to most other contaminants cannot be made currently, due to their low rate of detection in table-ready foods. Monitoring programs that use more sensitive study designs and population-based assessments for other subpopulations should be a priority for future research.

Adult↗
PubMed1977

Human tissue distribution of cyclodiene pesticides-Hawaii 1964-1973.

Data have been presented covering symptoms of acute exposure to cyclodiene pesticides in adults and infants in Hawaii. Varying concentrations of heptachlor epoxide, dieldrin, DDT, DDE, and DDD were found in human autopsy material, with the highest levels of heptachlor epoxide in bone marrow and liver and those of dieldrin in kidney and gonad. Maximum concentration of dieldrin in human milk was 0.25 ppm on an extracted lipid basis; in fetal tissues, 1.46 ppm; and in maternal tissues, 2.04 ppm. There was correlation between dieldrin concentration in household dust and human blood serum. The general baseline levels of cyclodiene pesticides were lower in Hawaii than the rest of the United States.

Autopsy↗
PubMed1970

[Insecticide resistance in bedbugs(Cimex lectularius) in Korea]

In the summer of 1969 from July through October, authors carried out a study of susceptibility in adult female bed bug(Cimex lectularius) in order to ascertain any development of resistance to insecticides in Korea. The test to DDT and Dieldrin was performed in laboratory by the continuous exposure of residues method, with standard impregnated paper used for adult mosqitoes. Some results so far obtained can be summarised as follows: 1. LC(50) were 2.839% in DDT and 0.167% in Dieldrin. 2. The resistance has been arisen 2.4~2.9 times in DDT and 1.6~2.4 times in Dieldrin as compared with London laboratory strain, but they were susceptible 1.4 times in DDT and 180 times in Dieldrin as compared to Israel resistance strain.

Journal Article↗
PubMed1970

[Susceptibility Of Cockroaches (Blattella Germanica Linneaus) To Various Insecticides]

During the period from May to October 1969, the authors carried out a series of tests with the aim to ascertain the present status of susceptibility of adult cockraoches to various insecticides. The tests on the susceptibility of cockroaches to dieldrin, D.D.V.P., Diazinon; Dibrom, Malathion and lindane were performed with the topical application and the residual film methods under the conditions of 26 degrees C and 80% of relative humidity. The insects tested were collected from Seoul City and were reared at the laboratory. Some of the important results so far obtained can be summarized as follows: 1. The median lethal doses (LD-(50)) of the five insecticides against female adult cockroaches were: 0.4 microgram/roach or 4.02 microgram/body weight (gm) by Dieldrin, 0.29/roach or 2.88 microgram/body weight (gm) by D.D.V.P., 0.29 microgram/roach or 2.96 microgram/body weight (gm) by Diazinon, 0.54 microgram/roach or 5.37 microgram/body weight (gm) by Dibrom, and 2.96 microgram/roach or 29.60 microgram/body weight (gm) by Malathion. And those against male adult cockroaches were: 0.18 microgram/roach or 3.29 microgram/body weight (gm) by Dieldrin, 0.27 microgram/roach or 4.89 microgram/body weight (gm) by D.D.V.P., 0.16 microgram/roach or 2.91 microgram/body weight (gm) by Diazinon, 0.49 microgram/roach or 8.97 microgram/body weight (gm) by Dibrom, and 1.32 microgram/roach or 24.19 microgram/body weight (gm) by Malathion. 2. The level of susceptibility of adult cockroaches to the insecticides tested was 1.0-1.6 times higher as compared with the results obtained on the Japanese Takashi strain. 3. The median knockdown times (LT-(50)) of the female adult cockroaches by insectcides at 1% concentration of 3 mg per square centimetre were 1.82 hours by Malathion, 1.36 hours by Diazinon, 0.56 hours by Lindane, 0.50 hours by Dibrom, and 2.56 hours by D.D.V.P. 4. Amarked difference was seen to exist between the males and the females. The female cockroaches were more resistant than the male to Dieldrin, Diazinon and Malathion.

Journal Article↗
PubMedDate not supplied

Dietary intake and residues of organochlorine pesticides in foods from Hsinchu, Taiwan.

The levels of contamination with various organochlorine pesticides (such as total HCH, heptachlor, heptachlor epoxide, aldrin, dieldrin, endrin, endosulfan, and total DDT) of different foods from 3 traditional markets were determined to estimate Taiwanese daily intake of organochlorine pesticides. Of the 18 organochlorine pesticides investigated, alpha-HCH, beta-HCH, lindane, delta-HCH, heptachlor, heptachlor epoxide, dieldrin, endrin, alpha-endosulfan, p,p'-DDE, and p,p'-DDT were detected at concentrations ranging from 0.26 to 10.2 ng/g wet weight. Contamination with organochlorine pesticides followed the order heptachlor > dieldrin > alpha-endosulfan > HCH isomers > heptachlor epoxide > DDT. Frequencies of detection of organochlorine pesticide residues ranged from 2.0 to 52.3%. alpha-Endosulfan was the most frequently detected organochlorine pesticide in the foods analyzed, followed by heptachlor epoxide (47.6%) and alpha-HCH (38.9%). Estimated daily intakes (EDIs) of organochlorine pesticides from foods were 1.137 micrograms for total HCH, 2.147 micrograms for heptachlor, 0.702 microgram for heptachlor epoxide, 0.624 microgram for endosulfan, 0.098 microgram for cyclodiene, and 0.541 microgram for total DDT. These EDIs were only 0.075% of the acceptable daily intake (ADI) for lindane, 47.5% of ADI for heptachlor and heptachlor epoxide, 0.045% of ADI for total DDT, and 1.01% of ADI for aldrin and dieldrin. Therefore, consumption of the foods analyzed does not pose a risk to consumer health.

Chromatography, Gas↗
PubMed1957

Toxicity of some newer insecticides to larvae and pupae of Culex fatigans Weidemann.

The toxicity of DDT, dieldrin, endrin, malathion, parathion, Systox and P4 to larvae and pupae of Culex fatigans has been studied. Two colonies of mosquitos were maintained for the purpose-one at 88 degrees +/-2 degrees F (31.1 degrees +/-1.1 degrees C) and 70%-80% relative humidity, and the other at 72 degrees +/-3 degrees F (22.2 degrees +/-1.7 degrees C) and 45%-55% relative humidity.For test purposes 25 larvae or pupae were exposed to acetone solutions of insecticides in 25 ml of water, and mortality counts were taken at the end of 24 and 48 hours. The percent mortality was plotted on a logarithmic dosage-probit paper and the LC(50) (the concentration required to kill 50%) was read from the slopes obtained. The confidence limits for LC(50) and the slope functions were worked out statistically.Of the insecticides tested, parathion was found to be the most toxic to larvae. The others in their order of toxicity were endrin, dieldrin, DDT, malathion, P4 and Systox. The LC(50) at 24 hours ranged from 0.003 parts per million (p.p.m.) for parathion to 0.18 for Systox. The third-instar larvae were more susceptible to insecticides than those in the fourth-instar stage.Pupae were more resistant to insecticides than larvae. Parathion and endrin gave LC(50)'s of 0.034 and 0.04 respectively. P4 and malathion gave very poor results. Dieldrin and Systox acted slowly on pupae, and the 48-hour mortality is given for these. DDT showed extremely low toxicity to pupae.DDT, dieldrin, endrin and parathion were more toxic to larvae reared and tested at the lower temperature than to those reared and tested at the higher. The temperature after exposure to DDT altered toxicity to a greater extent than the temperature at which the larvae had been reared.

Animals↗
PubMed2004

Toxicological studies of pesticides on cytoplasmic streaming in Nitella.

In the present study, changes in velocity of cytoplasmic streaming in the giant internodal cells of Nitella for varying concentration of the pesticides, 2,4-D, dieldrin, malathion, methyl parathion and endosulfan, were measured. Marked decrease in the velocity of cytoplasmic streaming was found at the concentrations of 0.01, 0.1, 1, 10 and 100mM. Dieldrin was the most toxic to all the pesticides investigated, followed by methyl parathion, endosulfan, malathion and 2,4-D. Threshold values for dieldrin, methylparathion, endosulfan, malathion and 2,4-D as indicated by the onset of decrease in the normal cytoplasmic streaming velocity were less than 6.25 x 10(-6), 2.5 x 10(-5), 5 x 10(-5), 5 x 10(-5) and 1.25 x 10(-5)M respectively. Cessation of streaming was noticed above 1mM in dieldrin and above 10mM when exposed to methylparathion and endosulfan. Cessation of streaming was not seen up to 100mM concentration of 2,4-D and malathion.

Cytoplasm↗
PubMed2001

[Malaria vector control in Cameroon: past, present, future. Reflections].

During the fifties, large scale malaria vector control projects based upon house spraying were implemented in Southern and Northern parts of Cameroon in line of malaria eradication concept. In the South, the pilot zone of Yaounde gathered about 150,000 inhabitants, in the forest area. First operations started in 1953 but the programme became actually operational in 1956. It was divided in two parts: the western part was treated with DDT, while the eastern one was treated with dieldrin. At the same time, the whole forested area was also treated with dieldrin until 1960. Yaounde itself was not treated because it was free of anopheles and malaria. House spraying in the pilot area of Yaounde was a complete success and plasmodic index dropped below 1%. The same success was observed in most of the southern treated areas. Unfortunatly dieldrin resistance of An. gambiae hampered this programme which stopped in 1960. The northem pilot project dealt with some 250,000 inhabitants around Maroua, in a savanna area. To avoid dieldrin resistance observed in 1956, DDT was selected and house spraying started in 1959. From a strictly operational point of view, the campaign was considered as a success. But after two years, it was noticed that plasmodic index remained still around the same value of 35% and the programme stopped. It was thus stated that according to available techniques it was not possible to reach the ultimate goal of eradication even when chemoprophylaxis (chloroquin + pyrimethamin) was added. The comparison between south (= success) and north (= failure) was very interesting as it underlined the big differences between epidemiological faces, an unaccepted concept at that time. Now ecological and epidemiological diversity is the well acknowledged. It also underlined the need of diversity of strategies according to the epidemiology of the disease and the ecology of its vector Vector control was then stopped for a while. In the eighties, Primary Health Care was promoted and malaria control shifted from vector to parasite control, vector control remaining as a prevention method. But chemioresistance of Plasmodium falciparum appeared and. quickly spread, at different levels, across the country. A new emphasis was therefore given to vector control thank to the newly developed technique of insecticide impregnated mosquito nets. Two kinds of studies were undertaken: - what people were actually doing in term of mosquito control at family level, the main reason and the costs as well as current use of mosquito nets - the efficacy of pyrethroid treated mosquito nets (IMN) in different areas of southern forested area against different malaria vectors: An. gambiae, An. nili, An. moucheti. It thus clearly appeared that IMN were very successful in sharply reducing malaria transmission aAd morbidity. But its promotion is limited by the current poor use of mosquito nets in Yaoundé (1 mosquito net for 27 "beds") while in Douala, where IMN are largely used against the bite of the huge population of Culex. quinquefasciatus, the implementation of the first riational centre for impregnation of mosquito net was a great success, as long as it was headed by a motivated and skill manager Impregnated mosquito nets appear thus as a tool of great efficacy but their sustainability is still matter of concern and promotional campaigns must be developed involving private and public, political and scientific spheres as well as the general population who should be encouraged to become partners and even actors of vector and malaria control at their household level.

Animals↗
PubMed1996

Current status of Anopheles stephensi response to various insecticides in some areas of the Thar desert.

Investigations on the current response of A. stephensi. to six insecticides viz. DDT, dieldrin, malathion, fenitrothion, propoxur and permethrin, were carried out in 3 districts i.e. Barmer, Jodhpur and Pali, of the Thar desert. The species was found resistant to DDT and dieldrin, partially resistant to malathion and susceptible to fenitrothion, propoxur and permethrin. Dieldrin and malathion resistance has been detected for the first time in the Thar desert. Lethal concentrations (LC50 & LC95) of DDT and dieldrin and lethal exposure times (LT50 & LT95) of malathion, fenitrothion, propoxur and permethrin have been determined. In some areas, the differences in LC50 and LT50 values of tested insecticides, except fenitrothion, were found statistically significant. Chi-square and regression tests have revealed the homogeniety and linear trend respectively in the response of A. stephensi to insecticides. The findings of the study indicate that organochlorine compounds can be used alternately in the spray operations.

Animals↗
PubMed1976

Organochlorine pesticides in the Hawaii Kai Marina, 1970-74.

Sediments, water, and oysters from the receiving waters of the Hahaione Valley, a suburban development in south-easter Oahu, Hawaii, were analyzed for organochlorine pesticidal compounds. The insecticides dieldrin, alpha- and gamma- chlordane, and p,p'-DDT were found in the study site environment. Levels were in the low parts per billion range for oysters and sediments and in the low parts per trillion range for water. During the past several years dieldrin residues in the marina study site have increased, even though the only activity known to influence pesticide levels in the valley is the chronic treatment for subterranean and dry wood termites. If present trends continue, dieldrin may pose a threat to biota of the aquatic environment. Findings have shown that residue levels of dieldrin and p,p'-DDT in the sediments are within the LD50 (median lethal dose) range for estuarine fish and thus may have a deleterious effect on bottom-feeding organisms. According to present standards of the Food and Agriculture Organization/World Health Organization, pesticide residue levels within the study site do not appear to constitute a health hazard to humans.

Animals↗
PubMedDate not supplied

Ion channels as targets for insecticides.

Most insecticides are neurotoxicants causing various forms of hyperexcitation and paralysis in animals. A variety of neuroreceptors and ion channels have been identified as the major target sites of these neurotoxic insecticides. This paper gives the highlights of some of the recent development in this area. Pyrethroids keep the sodium channel open for unusually long times causing a prolonged flow of sodium current. The prolonged sodium current elevates and prolongs the depolarizing after-potential which reaches the threshold membrane potential to initiate repetitive after-discharges. We have developed the method with which the percentage of sodium channel population that needs to be modified to cause repetitive after-discharges can be measured accurately. In rat cerebellar Purkinje neurons, only 0.6% of sodium channels needs to be modified for hyperexcitation resulting in a large toxicity amplification. This concept is applicable to other neuroactive drugs that act through the threshold phenomenon. The mechanisms of selective toxicity of pyrethroids in mammals and insects have been quantitatively determined to be due mainly to the different sensitivity of the sodium channels to pyrethroids and the negative temperature dependence of pyrethroid action on the sodium channels. The degradation of pyrethroids play only a minor role. The negative temperature dependence of pyrethroid action is due to the increased sodium current flow at low temperature. The major site of action of dieldrin and hexachlorocyclohexane is the GABA(A) receptor chloride channel complex. Dieldrin exerts a dual action, initial stimulation and subsequent suppression, and the latter is responsible for hyperexcitation of animals. Dieldrin stimulation requires the gamma2s subunit in the GABA receptor, whereas dieldrin suppression occurs in the presence or absence of the gamma2s subunit.

Animals↗
PubMed1994

Parkinson's disease and brain levels of organochlorine pesticides.

Epidemiological studies have suggested an etiologic relationship between pesticide exposure and Parkinson's disease (PD). Organochlorine pesticides were assayed in postmortem brain samples from 20 PD, 7 Alzheimer's disease (AD), and 14 nonneurological control cases. The three groups were similar in age at death, sex, and demographic variables. Only two of 16 pesticide residues screened were detected. A long-lasting residue of DDT (pp-DDE) was found in the majority of cases of PD and AD, as well as in all the control cases; pp-DDT was significantly more likely to be found in AD controls than the PD cases (Fisher's exact two-tailed, p = 0.04). Dieldrin was detected in 6 of 20 PD brains, 1 of 7 AD, and in none of 14 control samples. Despite the relatively small number of brains assayed, the association between Dieldrin and the diagnosis of PD was highly significant (p = 0.03). Dieldrin, a lipid-soluble, long-lasting mitochondrial poison, should be investigated as a potential etiological agent of Parkinsonism.

Age Factors↗
PubMed2007

Occupational exposure to organochlorine insecticides and cancer incidence in the Agricultural Health Study.

Organochlorine (OC) insecticides have been regulated as possible human carcinogens primarily on the basis of animal studies. However, the epidemiologic evidence is inconsistent. We investigated the relationship between cancer incidence and OC insecticide use among pesticide applicators enrolled in the Agricultural Health Study, a prospective cohort study of 57,311 licensed applicators in Iowa and North Carolina enrolled between 1993 and 1997. Information on ever use of 7 OC insecticides (aldrin, chlordane, DDT, dieldrin, heptachlor, lindane, toxaphene) was collected from a self-administered questionnaire at enrollment. Lifetime exposure-days to OC insecticides were calculated using additional data from a take-home questionnaire completed by 25,291 participants (44% of total). We found no clear evidence of an association between use of OC insecticides and incident cancers (N = 1,150) ascertained through December, 2002. When we focused on individual insecticides and structurally similar groups (aldrin and dieldrin; chlordane and heptachlor), significantly increased relative risks of some cancers were observed for use of some chemicals (rectal cancer and chlordane, lung cancer and dieldrin, non-Hodgkin lymphoma (NHL) and lindane, melanoma and toxaphene, leukemia and chlordane/heptachlor). Some significant decreased relative risks were also observed (colon cancer and aldrin; overall cancer and heptachlor). In conclusion, we did not observe any clear relationship between cancer risk and the use of OC insecticides. Our chemical-specific findings are based on small numbers and multiple comparisons, and should be interpreted with caution; however, some observed associations (lindane and NHL, chlordane/heptachlor and leukemia) are supported by previous evidence.

Adult↗