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Cyclodiene insecticides-induced changes in the central depressive effect of chlorpromazine in rats.

Spontaneous motor activity (SMA), conditioned avoidance response (CAR), muscle coordination (MC) and pentobarbital sleep were tested in rats treated orally for 90 days with tolerated doses of the cyclodiene insecticides, aldrin (1 mg/kg) and endosulfan (2 mg/kg). The same tests were repeated in similarly treated animals after injecting chlorpromazine (4 mg/kg, i.p.). Both the insecticides shortened pentobarbital sleeping time indicating their microsomal enzyme inducing property. Aldrin suppressed SMA, CAR and MC, whereas endosulfan stimulated SMA, inhibited CAR and unaltered MC. However, their concurrent action with CPZ did not result in change in the central depressive effects of the latter, but its potency during the course of its action was altered. Its potency 15 min after injection was greater and 60-180 min later was lesser in these animals than that observed in control animals. This finding was interpreted to suggest that aldrin and endosulfan has quickened the biotransformation of CPZ and thereby shortened its duration of action. A temporary promotion of its potency was accounted to its active metabolites, since prior to inactivation, CPZ is known to be metabolized by the microsomal enzymes to active compounds.

Aldrin↗

Occurrence of pesticides in fish tissues, water and soil sediment from Manzala Lake and River Nile.

Pesticides constitute the major source of potential environmental hazard to man and animal as they are present and concentrated in the food chain. This study was conducted on 136 samples of water, sediment and fish for detection and determination of pesticide residues in this ecosystem. Highly significant differences were found in levels of Indian, heptachlor, endrin, dieldrin, P,P'-DDE and propoxur in River Nile water when compared with that of Manzala Lake. Levels of Indian, endrin, malathion and diazinon were significantly higher in soil sediment of Manzala Lake, while the levels of heptachlor, aldrine, P,P'-DDE, DDT, parathion, propoxur and zectran were significantly higher in soil sediment of River Nile. Boury fish of Manzala Lake contained higher levels of heptachlor, aldrin, P,P'-DDE and malathion, while boury fish of River Nile contained a higher level of zectran only. This survey, thus indicated that Manzala Lake and even the River Nile which was used as control are heavily contaminated with chlorinated hydrocarbons (Indian, heptachlor, aldrin, endrin, dieldrin, P,P'-DDE and DDT), organic phosphorus compounds (malathion, dimethoat, diazinon and parathion) and carbamate pesticides (propoxur and zectran).

Agriculture↗

Organochlorine pesticides and polychlorinated biphenyls in foodstuffs from Asian and oceanic countries.

Public concern about the adverse environmental and human health impacts of organochlorine contaminants led to strict regulations on their use in developed nations two decades ago. Nevertheless, DDT and several other organochlorine insecticides are still being used for agriculture and public health programs in developing countries in Asia and the South Pacific. As a consequence, humans in this region are exposed to greater dietary levels of organochlorines. In this review, published information on organochlorine concentrations in foodstuffs from South and Southeast Asia and Oceanic countries has been compiled. Foodstuffs that contribute to human exposures and dietary intakes of organochlorines were examined, and the data compared with those reported from more developed nations. Among various developing countries in Asia, considerable information on organochlorines in foodstuffs has been available from India since the late 1960s. DDT and HCH were the major insecticides in Indian foodstuffs. Concentrations of these insecticides have declined more than two orders of magnitude in farm products, such as food grains and vegetables, in two decades. Milk and milk products are the major sources of dietary exposure to DDT and HCH in India. The residues of these insecticides in dairy products were close to or above the MRLs of the FAO/WHO. Dietary intake of DDT and HCH by Indians was > 100 fold that in more developed nations. Sporadic incidences of greater concentrations (> 1 microgram/g) of aldrin, dieldrin, and heptachlor have been measured in Indian vegetables. Untreated surface waters could be a potential source of DDT and HCH exposure. In most Southeast Asian countries DDT was the common contaminant in animal origin foodstuffs. The higher percentage of p,p'-DDT in meat and fish from Southeast Asian countries, except Japan and Korea, indicated the recent use of DDt in vector control operations. Dietary intakes of DDt and HCH in Southeast Asia were an order of magnitude less than those of Indians but 5- to 10 fold greater than in more developed nations. In addition to DDT, aldrin and dieldrin were prominent in meat collected from Thailand and Malaysia. Aquatic food products from more industrialized countries, such as Japan, South Korea, Hong Kong, and Taiwan, contained significant levels of PCBs. In South Pacific countries, particularly in Australia and New Zealand, chlordanes and PCBs were the most prevalent organochlorines in foodstuffs. Food contamination by DDT, HCH, aldrin, and dieldrin was less than in developing countries in Asia but greater than in the U.S. and Japan. Intake of PCBs in Australia was greater than in the U.S. Meat and fish were the major sources of organochlorine exposure by Australians. Human dietary intake of organochlorines has been declining more slowly in developing countries in Asia. Current intakes were at least 5- to 100 fold greater than those in more developed nations, suggesting a greater risk from organochlorine exposure. Factors such as malnutrition, common among rural poor in developing nations, can increase these risks. Of greatest concern is the magnitude of exposure to organochlorines to which infants and children are subjected through human and dairy milk. The estimated intake of DDT by infants was at least 100 fold greater than the ADI of the FAO/WHO. In addition to DDT, excessive exposures to HCH and dieldrin may cause potential health effects in infants because they are more vulnerable to toxic effects. The design and implementation of appropriate epidemiological studies and their integration with monitoring of human, food, and environmental samples would be a major step in assessing the risks of organochlorine residues in foods and controlling or eliminating them. With the continued globalization of trade in food products, and the concomitant risk that food contaminated through point-source pollution may be widely distributed, identification of sources and their control should be matters of

Asia↗

Genetic analysis of aflatoxin B1 activation in rat hepatoma cells.

We present a strategy to elucidate the rate-limiting steps in activation of carcinogenic compounds by cytochromes P450. The principle was to select Reuber rat hepatoma cells for resistance to a procarcinogen. The hypothesis was that resistant cells should be systematically deficient in the P450 enzyme(s) involved in the activation process. Here we present an example of the use of this approach using aflatoxin B1 (AFB1), a potent hepatocarcinogen, as the selective agent. Parental cells as well as individual and pooled colonies selected for AFB1 resistance from three independent rat hepatoma lines were characterized for their content of 1) mRNA hybridizing to cDNA and/or oligonucleotide probes for cytochromes P450IIB1, P450IIB2 and albumin; and 2) aldrin epoxidase activity. Parental aflatoxin B1-sensitive cells were shown to express P450IIB1 but not P450IIB2. The majority of the aflatoxin B1-resistant clones failed to accumulate cytochrome P450IIB1 mRNA and expressed no or only very low aldrin epoxidase activity. Albumin mRNA levels remained unchanged, demonstrating that loss of expression of cytochrome P450IIB1 was not a consequence of a general dedifferentiation event. A revertant population showing restoration of both cytochrome P450IIB1 mRNA accumulation and aldrin epoxidase activity was fully sensitive to aflatoxin B1. The correlation between expression of cytochrome P450IIB1 and sensitivity to aflatoxin B1 in both parental cells and revertants strongly suggests that cytochrome P450IIB1 is a major contributor to the activation of aflatoxin B1 in rat hepatoma cells. The kind of strategy described here could be applied to other compounds that become cytotoxic for hepatoma cells following activation by cytochromes P450.

Aflatoxin B1↗

Effect of ofurace, oxadixyl, and alachlor on xenobiotic biotransformation in the rat liver.

Ofurace, oxadixyl, and alachlor were studied for their effect on hepatic xenobiotic biotransformation in male rats by dosing i.p. with 1 or 100 mg/kg of chemical for 7 days. Ofurace decreased ethoxyresorufin-O-deethylase and aniline p-hydroxylase activities but induced ethoxycoumarin-O-deethylase activity. Glutathione S-transferase and aminopyrine N-demethylase activities responded in a non dose-dependent manner, while cytochrome P-450 content and aldrin epoxidase activities were unchanged. Oxadixyl induced P-450 content, and ethoxycoumarin-O-deethylase and aminopyrine N-demethylase activities. It left ethoxyresorufin-O-deethylase, aldrin epoxidase and epoxide hydrolase activities unchanged and decreased aniline p-hydroxylase activities. Alachlor induced all activities excepting aldrin epoxidase (no change) and aniline p-hydroxylase (decreased). The data indicate that each of these acylanilide pesticides interacts with the monooxygenase system but with differing patterns.

Acetamides↗

Organochlorine pesticides in Argentinian butter.

Organochlorine pesticide residues were analysed in 150 samples of butter collected from several places in the cities of Santa Fe and Rosario (Argentine Republic) over a period of 18 months. Pesticides analysed in butter were: HCH (alpha and gamma isomers), heptachlor and its epoxide, aldrin, dieldrin, and DDT (p,p' DDE, o,p' DDT and p,p' DDT). Most samples contained residues of gamma-HCH (Lindane) and heptachlor (92% and 78%, respectively); alpha-HCH and aldrin were detected in 58% and 55% of samples; dieldrin, heptachlor epoxide, DDT isomers were found in few cases (30%). Mean values of pesticides residues in butter fat were: sigma HCH 0.029 ppm; sigma heptachlor 0.064 ppm; sigma aldrin 0.11 ppm and sigma DDT 0.024 ppm. Residue levels exceeded the limits prescribed by the Food and Agricultural Organization/World Health Organization in only very few cases.

Argentina↗

Residues of organochlorine pesticides in fruits, vegetables and tubers from Nigerian markets.

Residue levels of organochlorine pesticides have been determined in raw fruits, vegetables and tubers from markets in Nigeria. In the fruits, total HCH, aldrin and total DDT were detected in 77, 38 and 30% of all samples, respectively. In the vegetables, total HCH, HCB, total DDT and aldrin were detected from 95, 53, 50 and 30%, respectively, of all samples. Aldrin + dieldrin, total HCH, and total DDT were detected from 98, 79 and 49%, respectively, of all tuber samples. Other pesticides were below their detection limits. The average levels were generally low and none were above the FAOs maximum residue limits.

Agriculture↗

Gas chromatographic determination of organochlorine pesticides in cow milk.

A gas chromatographic method of use in determining the following organochlorine pesticides in cow milk has been adapted and validated: alpha-hexachlorocyclohexane (alpha-HCH), beta-HCH, lindane, delta-HCH, hexachlorobenzene, aldrin, heptachlor, heptachlor epoxide, mirex, 2,4-dichlorodiphenyltrichloroethane (2,4-DDT), 4,4-DDT, 2,4-dichlorodiphenyldichloroethane (2,4-DDD), 4,4-DDD, 2,4-dichlorodiphenylethane (2,4-DDE) and 4,4-DDE. The method studied consists of three steps: the extraction of fat by centrifugation, mixing with anhydrous sodium sulfate, and transfer to a glass column and elution with hexane; purification of the extract via concentrated sulfuric acid treatment; and determination of the organochlorine pesticides by gas chromatography equipped with an electron capture detector. The analytical parameters determined to estimate the quality of the method yielded the following results: correlation coefficients (r) of the calibration curves were greater than 0.996, the variation coefficients of the response factors were less than 4.90%--with the exception of aldrin (5.53%) and lindane (5.75%)--the relative standard deviation of the slope (Sm rel) being < or =1.52%. Zero was included in the confidence limits of the independent term range. The method repeatability and reproducibility values were < or =4.73% and < or =5.79%, respectively. The recovery values of the pesticides analyzed were in the range of 81.92% (alpha-HCH) to 105.49% (4,4-DDT), except in the case of aldrin and heptachlor epoxide, which yielded recovery values of under 40%. The quantification limits of the method were < or =1 ng/g, with the exception of mirex (5 ng/g).

Animals↗

Organochlorine compounds in adipose tissue of Greenlanders and southern Danes.

Abdominal fat tissue samples from the general population of Greenland and from southern Denmark were analyzed for o,p'-DDE and p,p'-DDE [1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene], p,p,-DDT [1,1,1-trichloro-2,2-bis(p-chlorophenyl)-ethane], o,p'-DDT and p,p'-DDD [1,1-dichloro-2,2-bis(p-chlorophenyl)ethane], lindane (1,2,3,4,5,6-hexachlorocyclohexane), aldrin (1,2,3,4,10,10-hexachloro-1,4,4a,5,8,8a-hexahydro-endo-exo-1,4:5,8-dimethanonaphthalene), dieldrin (1,2,3,4,10,10-hexachloro-6,7-epoxy-1,4,4a,5,6,7,8,8a-octahydro-endo-exo-1,4:5,8-dimethanonaphthalene), heptachlor (1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro-4,7-methanoindene), heptachlor epoxide, and polychlorinated biphenyls (PCBs). Fat tissue from Greenlanders contained significantly higher amounts of p,p'-DDE (p less than or equal to 0.05), p,p'-DDT (p less than or equal to 0.01), and total DDT (SIGMA DDT, the sum of DDT and its metabolites) (p less than or equal to 0.01) than southern Danes. Lindane, aldrin-like residue, dieldrin heptachlor-like residue, heptachlor epoxide, and PCBs were present in adipose tissue of both groups and there were no significant differences between the groups. The p,p'-DDE level in Greenland was lower than that in the United States, eastern Europe, and India. Among Greenlanders of different ages the highest sigma DDT was found in the age group of 22-45 yr; the content of PCBs increased with age. Among southern Danes the highest sigma DDT was found in a higher age group than in Greenlanders. Among Greenlanders the content of aldrin-like residue decreased with age and that of dieldrin increased with age. A significant correlation was found (on the basis of wet weight) between p,p'-DDE and PCB content in southern Danes (p less than or equal to 0.02). The correlation between sigma DDT and PCB content was also significant in this population (p less than or equal to 0.01). These two relationships were not significantly correlated for the Greenlanders. The DDE/PCB and sigma DDT/PCB ratios were higher in Greenlanders than in southern Danes. These ratios are age-dependent and are highest in the age group 22-45 yr among the Greenlanders. A low DDE/PCB ratio and a low sigma DDT/PCB ratio have been proposed as markers for industrialization. In Greenlanders p,p'-DDE represented about 70% of sigma DDT. For southern Danes this level was about 90%. The data obtained are presented and discussed on the basis of both lipid and wet weight levels.

Adipose Tissue↗

Rat hepatic microsomal enzyme induction by pretreatment with toxaphene and toxaphene fractions.

The levels of hepatic microsomal induction caused by toxaphene were determined. Young Sprague-Dawley rats (70 g) were administered toxaphene (ip injection, daily for 5 d) at 0, 5, 25, and 100 mg/kg. All doses caused increases in liver/body weight ratio, cytochrome P-450 level, aminopyrine demethylation, and aldrin epoxidation. The aldrin epoxidase activity increased almost 700% at the 100-mg/kg dose. Toxaphene was separated into nonpolar (S-A) and polar (S-B) fractions and administered as before at 25 mg/kg. All treatments caused significant increases in cytochrome P-450, aminopyrine demethylation, and aldrin epoxidation. A comparison of the treatments, however, did not reveal any significant differences between the treatments.

Animals↗

The expression of different monooxygenases supported by cytochrome P-450 in neonatal rats and in primary fetal hepatocytes in culture.

In rat liver, the perinatal development of various monooxygenase activities follows different patterns, depending upon the reaction studied. The ontogeny of the 6 beta-, 7 alpha- and 16 alpha-testosterone hydroxylase activities differs very significantly. Aldrin epoxidase and steroid-metabolizing monooxygenases are expressed in primary fetal rat liver cells in culture after treatment in vitro with dexamethasone. Testosterone is not metabolized by the control cells and is hydroxylated on the 6 beta and 16 alpha positions following the addition of corticoids to the culture medium. The dose and time curves vary according to the hydroxylated position of the steroid. Aldrin epoxidase activity is nearly undetectable in the control cells, but is present and is inducible by phenobarbital following treatment with the corticoid. Phenobarbital induces aldrin epoxidase in the absence of dexamethasone in the culture medium, providing that the cells are pretreated with the corticoid for 48 h. The use of antibodies against the main cytochrome P-450 species purified from adult and phenobarbital-treated rats confirms that a similar cytochrome P-450 can be induced in fetal cells in culture. The perinatal regulation of biological events, such as the expression of the monooxygenases, can be reproduced in fetal rat liver cells in culture; such a model constitutes a unique tool for studying the biochemical mechanisms which control these phenomena.

Animals↗

Organochlorine pesticide residues in human milk in Kayseri.

In this study: dichlorodiphenyltrichloroethane (DDT) and its metabolites [DDT + dichlorodiphenyl-dichloroethylene (DDE)], BHC (HCH) and their main isomers such as alpha, beta, gamma BHC, aldrin and its metabolite dieldrin, heptachloride, heptachloride epoxide, were investigated in 51 samples of breast milk of 51 lactating women during 1988. The ages of the mothers, who were working in agriculture, ranged from 17 to 33 y (mean 24.2 y). The concentrations of hexachlorobenzene (HCB), alpha BHC, beta BHC, gamma BHC, heptachloride, aldrin, heptachloride epoxide, pp'DDE, dieldrin, op'DDT, pp'DDT were found as 84 +/- 23, 96 +/- 20, 522 +/- 120, 156 +/- 20, 198 +/- 130, 47 +/- 9, 11 +/- 4, 2389 +/- 280, 6.7 +/- 3, 70 +/- 12, 410 +/- 60 micrograms kg-1 milk, fat, respectively, measured by gas chromatography (GC) method. The concentrations of chlorinated pesticides in human milk samples from Kayseri were compared with similar data obtained from other countries. The amounts of total BHC and aldrin derivatives were below the acceptable daily intake (ADI), whereas the amount of total DDT derivates was above, of the World Health Organization (WHO).

Adolescent↗

Oxidase activities in macrocyclic-resistant and -susceptible Haemonchus contortus.

The role of oxidative metabolism in resistance to macrocyclic lactones in Haemonchus contortus was examined by measuring activities toward 2 model cytochrome P450 substrates, aldrin and ethoxycoumarin, in a susceptible and a resistant isolate of the parasite. Microsomal preparations from larvae and adults of the 2 isolates showed no differences in levels of NADPH- or cumene hydroperoxide-supported aldrin epoxidase or ethoxycoumarin O-deethylase activities. Intact adult nematodes showed an ability to catalyze the epoxidation of significant amounts of aldrin, although the nature of the enzyme group responsible was unknown. This epoxidase activity was greater in adults of the susceptible isolate. It is apparent that oxidase activities toward the 2 substrates are not enhanced in the resistant isolate, suggesting that the observed resistance to macrocyclic lactones may not involve enhanced oxidative metabolism.

7-Alkoxycoumarin O-Dealkylase↗

Pesticides and the environment.

In the period 1981-2000, an investigation was conducted on organochlorine insecticide (OCI) residues in the environment and their effects on human health. The analyses encompassed drinking and surface waters, air, foodstuffs, ready-made meals, human serum and human autopsy material. OCI residues were not detected in drinking water originating from great distributive systems in Vojvodina (purified and conditioned water) but in some sub-artesian wells there were HCH and aldrin residues. OCI residues were quantified in surface water of the river Danube which is in the required group, except for HCH in 1990/91, when it was in the III-IV group. Air was analyzed in Novi Sad, Zrenjanin, Kikinda, Beojin and Apatin. OCI residues are regularly tested in Zrenjanin (1996-2000): the most frequently detected are: HCH residues (37.83% samples), lindane (21.72% samples), heptachlor (17.60% samples) and rarely DTD and aldrin; aldrin (in traces), heptachlor and HCH were detected in Novi Sad. Heptachlor, lindane and HCH were also rarely determined in Kikinda. OCI have an affinity for fat tissues and their residues can be found particularly in foodstuffs originating from animals. They are not eliminated by thermal processing and it was established in pre-school institutions, student restaurants and homes for the aging; most frequently detected was p,p 'DDE isomer, rarely p,p 'DDT as well as HCH and rarely lindane. Although use of OCI is forbidden, due to their long persistence in the environment, they can be found in human tissues, which was proved by human serum analyses. Analyses of human autopsy material indicated presence of DDT metabolite--p,p 'DDE as well as lindane in all analyzed samples (brain, liver, fat and tumorous tissues).

Environmental Pollutants↗

Evidence for a PCN-P450 enzyme in chickens and comparison of its development with that of other phenobarbital-inducible forms.

Of four monoclonal antibodies to purified rat liver cytochrome P450s, including those from 3-methylcholanthrene-, phenobarbital-, ethanol-, and pregnenolone-16-alpha-carbonitrile-treated rats, only the monoclonal antibody against pregnenolone-16-alpha-carbonitrile-inducible P450 immunodetected proteins in chicken liver microsomes after blotting from sodium dodecyl sulfate-polyacrylamide gels. This protein migrated identically with the pregnenolone-16-alpha-carbonitrile-inducible P450 detected in microsomes from dexamethasone-treated rats. It was most predominant in liver microsomes from chickens at 1 day posthatching, whereas much lower levels were observed in the embryo and at 36 days posthatch. Phenobarbital and dexamethasone were both effective inducers of this protein. The developmental profile and induction by phenobarbital and dexamethasone of several cytochrome P450-associated catalytic activities were compared with those of the immunodetected protein. Chicken liver microsomal erythromycin demethylase, a characteristic activity of rat pregnenolone-16-alpha-carbonitrile-inducible P450, was similar in developmental profile and induction to the immunodetected protein, with a high degree of augmentation at 1 day posthatch compared with that in the embryo and at 36 days posthatch; aldrin epoxidase, benzphetamine demethylase, ethylmorphine demethylase, and aminopyrine demethylase were more similar to each other in development and induction and were less well correlated with the immunodetected protein. This evidence suggests the presence in chicken liver of at least two types of P450, one a form related to the pregnenolone-16-alpha-carbonitrile-inducible P450 family. All of the catalytic activities were induced after pretreatment of chickens with phenobarbital but aldrin epoxidase was most effectively induced. Aldrin epoxidase was also detected in microsomes from untreated embryos as early as 7 days of incubation. Erythromycin demethylase was the only catalytic activity induced by dexamethasone. There was a trend of increased specific activity toward all the substances after hatching, indicating a more efficient P450 system, possibly due to a sharp increase in some isozymes, including the form from the pregnenolone-16-alpha-carbonitrile-inducible P450 family. This evidence for a pregnenolone-16-alpha-carbonitrile-inducible P450 in chickens agrees with sequence information that suggests the early evolution of this form and demonstrates the suitability of the chicken for studies of P450 evolution.

Animals↗

Organochlorine insecticide residues in field soils of the Kitakyushu district--Japan 1970-74.

Residues of organochlorine insecticides were monitored in field soils of the Kitakyushu District, Japan, from 1970 to 1974, before and after the insecticides were banned from agricultural fields. The arithmetic mean (AM) and geometric mean (GM) of BHC reached maximum levels in 1970 and 1971, then decreased rapidly during 1972 and 1974. Among BHC isomers, beta-BHC had highest mean levels and was therefore thought to be the most persistent of the isomers in field soils. Residues of aldrin, dieldrin, and endrin peaked in 1970 and/or 1971, and then decreased yearly. The percentage of sites which had aldrin contamination have decreased; those with dieldrin contamination have increased. Mean values of p,p'-DDE, p,p'-DDT, and sigmaDDT declined more slowly than did BHC and cyclodienes. Values of DDT and its related compounds were higher than were those of BHC, aldrin, dieldrin, and endrin. The residues of p,p'-DDE were most frequently detected of the DDT compounds.

Chromatography, Gas↗

Induction of hepatic cytochrome P-450 by phenobarbital in semi-aquatic frog (Rana pipiens).

Hepatic microsomal cytochrome P450 (equivalent to rat P4502B1 isozymic form, a CYPIIB gene product) can be induced by pentobarbital (PB) in the adults of the semiaquatic frog, Rana pipiens (as in other terrestrial vertebrates), but not in adults of the aquatic frog Xenopus laevis or in bluegill sunfish (Lepomis macrochirus). The activity of PB-induced P450 (2B1) towards aldrin and pentoxyresorufin increases respectively by about 2- and 10-fold. This enzyme is not inducible during larval and postlarval stages of R. pipiens. However, cytochrome P4501A1 (CYPIA1 gene product) is inducible by beta-naphthoflavone in all these species. Both CYPIA and CYPIIB genes are expressed, as determined by the catalysis of their protein products, during larval, postlarval, and adult stages of R. pipiens. The concentration of P450 increases slightly during the postlarval stages until the adult stage, ready to migrate to land, is reached. This increase seems to be mostly due to 2B1-type cytochrome P450 as judged by a large increase in aldrin epoxidase but not of 7-ethoxyresorufin O-deethylase activity. It is hypothesized that the evolution of true terrestrialness, and not the evolution of air-breathing lungs alone, is required for the transcriptional activation of CYPIIB gene by PB.

Age Factors↗

Uptake and persistence of pesticides in cultured human cells.

The uptake and persistence of 14C-labeled pesticides in cultur-s of human embryonic lung diploid cells were studied. Chlordimeform, DDT, parathion, aldrin and dieldrin were selected as test compounds. Results obtained from these experiments divided the chemical into two groups. The first group consisted of three chemical DDT, aldrin and dieldrin which are generally classified as persistent insecticides while the second group was composed of chlordimeform and parathion, generally considered to be non-persistent insecticides. The rate of initial cellular incorporation of first group was approximately 20 to 70 times greater than the non-persistent insecticides. During the course of an incubation, the amounts of pesticide taken up by the cells decreased gradually.

Aldrin↗