Search PubMed⌕ Search

SEARCH · Search PubMed

Results for “Endrin”

Search indexed PubMed citations on genomics, clinical trials, systematic reviews and public health. Explore titles, authors and supplied subject terms, then open the PubMed record.

Quote a phrase for an exact phrase match. Source license links do not imply unrestricted reuse.

At least 73 records · Page 4Linked to original sources

Reductive degradation of dieldrin and endrin in the field using acidified zinc.

The reductive dechlorination of dieldrin and endrin was investigated as a possible procedure for field disposal of small quantitites of these pesticides. The objective was to convert the parent compounds to environmentally less objectionable materials. Emulsifiable concentrate formulations of the pesticides in a soil slurry were mixed with powdered zinc, dilute acetic acid, and acetone to facilitate reaction. Analysis of the mixtures by GC-MS indicated essentially complete conversion of endrin and partial conversion of dieldrin to products probably formed by replacement of the bridge anti chlorines with hydrogen. Partial confirmation of the desired anti dechlorodieldrin product was made by nmr. Disappearance of the parent compounds and production of conversion products was monitored for 2 1/2 years by GC in an outside soil plot, and accelerated destruction of parent compounds was achieved by the treatment. By analogy to the bridge anti dechloro products of aldrin and isodrin, the anti dechloro products probably are much less toxic than the parent compounds and are therefore environmentally less objectionable.

Dieldrin↗

Detoxication and bioactivation of endrin in the rat.

1. Rats exhibit a sex difference in the rate of metabolism of endrin. 2. The major metabolite in both sexes is anti-12-hydroxyendrin which is excreted via the bile as the glucuronide. Male rats produce the metabolite at a higher rate than do females. 3. trans-4,5-Dihydroisodrin-4,5-diol is a minor metabolite. A mechanism for its formation is discussed. 4. There is a sex difference in the production and excretion of 12-ketoendrin which is observed as a urinary metabolite in male rat; the major urinary metabolite in female rats is anti-12-hydroxyendrin O-sulphate. 5. syn-12-Hydroxyendrin was not detected but may be an intermediate in the formation of 12-ketoendrin. 6. The formation of 12-ketoendrin is related to the acute toxicity of endrin.

Adipose Tissue↗

Improved cleanup technique for the estimation of endosulfan and endrin residues.

An improved cleanup technique has been developed for the extraction of endosulfan and endrin from crops. The technique involves the use of Nuchar C-190N as adsorbent and a mixture of n-hexane and acetone (4+1) as the eluting solvent. The mean percentage recoveries of endosulfan (I and II) and endrin from plant tissue extracts fortified at levels of 0.5-2.0 ppm varied from 86 to 102 and 97 to 100, respectively.

Adsorption↗

[Endrin poisoning].

We present the case of a fifteen months female patient, who accidentally ingested "Endrin Helios" (cyclodiene organochlorinated pesticide) surviving this event. Clinical manifestations were generalized seizures without neither neurologic or hepatic damage. A review is made about the mechanism of intoxication with the toxic and also about the publications dealing with endrin.

Endrin↗

Endrin toxicosis in a cat.

Endrin toxicosis was believed responsible for the sudden death of a cat. Stomach contents contained bird remains, and chemical analysis revealed 233 micrograms of endrin/g. The cat's owner had been using an avicide on the premises just before the cat's death. Endrin is an effective pesticide for control of insects, rodents, and birds. It poses a problem with secondary poisoning in other animals.

Animals↗

[Fatal endrin poisoning].

Endrin is a cycladine organic chloride insecticide responsible for fatal poisoning due to food contamination, suicide or occupational cause. The case of an 18 months old infant who ingested Endrin that was being used at home by his parents as raticide is reported. There appeared sudden convulsive crises, coma and death within 24 hours. The pathological findings were unspecific. Experimental studies and clinical observations of other authors that are coincidental with the symptoms shown by this child are discussed. The possible etiopathogenesis of this poisoining, together with the necessity to control this type of toxics, for which there is no antidotal treatment, are also discussed.

Accidents, Home↗

Food safety program. Endrin monitoring in the Mississippi river.

Twelve successive monthly samplings and analyses of representative fish and shellfish and of mud and water from the lower Mississippi River showed neither a high concentration of endrin nor a time-ordered change in the concentration. The general absence of endrin from the samples indicated no significant contamination.

Animals↗

Degradation of endrin, aldrin, and DDT by soil microorganisms.

Twenty microbial cultures which had been shown to degrade dieldrin were tested to determine their ability to degrade endrin, aldrin, DDT, gamma isomers of benzenehexachloride (gamma-BHC), and Baygon. All isolates were able to degrade DDT and endrin, whereas 13 degraded aldrin. However, none of them was able to degrade Baygon or gamma-BHC.

Arthrobacter↗

The effect of in vivo exposure of endrin on the activities of acid, alkaline and glucose-6-phosphatases in liver and kidney of Ophiocephalus (Channa) punctatus.

The effect of in vivo exposure of a sublethal concentration (0.01 mg/l) of endrin on the activities of acid, alkaline and glucose-6-phosphatases in the liver and kidney of Ophiccephalus punctatus was studied. The period of exposure was twenty days. In the liver, alkaline phosphatase and glucose-6-phosphatase activities were decreased but acid phosphatase was stimulated. Kidney showed stimulation in the activity of all the three phosphatases.

Acid Phosphatase↗

In vivo effect of endrin on three phosphatases in kidney and liver of the fish Ophiocephalus punctatus.

The effect of endrin (0.030 ppm) on the acid phosphatase, alkaline phosphatase and glucose-6-phosphatase activities in the kidney and liver of a teleost fish, Ophiocephalus (Channa) punctatus has been studied. The period of exposure was twenty days. An increase in the acid phosphatase activity is noted in the two tissues examined here. There is no significant change in the activity of alkaline phosphatase in kidney while in liver the enzyme is inhibited. In the kidney glucose-6-phosphatase showed a slight increase in activity but it is inhibited in liver.

Acid Phosphatase↗

Acute toxicities of toxaphene and endrin to larvae of seven species of amphibians.

Seven species of amphibian larvae were exposed to toxaphene and endrin in a continuous-flow dosing system to determine differences in sensitivity to the two compounds, EC50 and LC50 estimates varied from those for Rana sphenocephala by no more than one order of magnitude when calculated on the basis of intended concentrations. Removal of pesticides from water by the test animals was significant and it makes interpretation of results difficult. Continuous-flow toxicity tests conflict with the adaptations of amphibian larvae for static water; use of such tests for amphibians requires further evaluation.

Ambystoma↗

Excretion of formaldehyde, malondialdehyde, acetaldehyde and acetone in the urine of rats in response to 2,3,7,8-tetrachlorodibenzo-p-dioxin, paraquat, endrin and carbon tetrachloride.

Formaldehyde (FA), acetaldehyde (ACT), malondialdehyde (MDA) and acetone (ACON) were simultaneously identified in urine, and their excretion quantitated in response to chemically induced oxidative stress. Urine samples of female Sprague-Dawley rats were collected over dry ice and derivatized with 2,4-dinitrophenylhydrazine. The hydrazones of the four lipid metabolic products were quantitated by high-performance liquid chromatography on a Waters 10-microns mu-Bondapak C18 column. The identities of FA, ACT, MDA and ACON in urine were confirmed by gas chromatography-mass spectrometry. An oxidative stress was induced by orally administering 100 micrograms/kg 2,3,7,8-tetrachlorodibenzo-p-dioxin, 75 mg/kg paraquat, 6 mg/kg endrin or 2.5 ml/kg carbon tetrachloride to rats. Urinary excretion of FA, ACT, MDA and ACON increased relative to control animals 24 h after treatment with all xenobiotics. The system has wide-spread applicability to the investigation of altered lipid metabolism in disease states and exposure to environmental pollutants.

Acetaldehyde↗

Endrin toxicity in cagebirds.

The deaths of approximately 320 cagebirds (finches, doves, quails) were found to be due to ingestion of panicum seed (Panicum miliaceum) contaminated with endrin. Most birds were found dead but some showed flight instability prior to death. No gross or microscopic lesions were found in necropsied birds.

Animals↗

Rapid method for extracting aldrin, dieldrin, and endrin from visceral material.

A simple method is described for purifying aldrin, dieldrin, and endrin from visceral material by using a Celite column. Celite retains all interfering materials including Lipids whereas the chlorinated Insecticides are eluted from the column with n-hexane. This extract can be used directly for gas chromatographic analysis.

Adsorption↗

[Determination of aldrin, dieldrin and endrin in the air by gas chromatography].

A gas chromatographic method of determination of aldrin, dieldrin and endrin in air has been developed. The method involves trapping in ethylene glycol, extraction with hexane and determination by electron capture gas chromatography on a Gas Chrom Q column coated with 15% QF-1/10% DC-200. The determinability of the method amounts to 0,0015-0,003 mg/m3.

Air Pollutants↗

p,p'-DDE, polychlorinated biphenyls, and endrin in oldsquaws in North America, 1969-73.

Organochlorinated compounds were monitored in oldsquaws (Clangula hyemalis) and their food from Lake Michigan between October and May, 1969-72; in adult oldsquaws, eggs, young, and food from northwest Hudson Bay in 1971; and in oldquaws from five wintering areas other than Lake Michigan in 1971-73. Analyses were conducted on 300 carcasses, 14 wings, 29 gullet samples, and 11 clutches. Average residues in carcasses from Lake Michigan ranged from 4 to 107 ppm PCBs, 2 to 42 ppm DDE, and less than 0.1 to 0.7 ppm endrin. Differences in DDE levels occurred between several sex and age classes during December on Lake Michigan; these differences were not apparent in the spring. Increases in DDE and PCB residues for oldsquaws occurred on Lake Michigan between December and May. DDE residues in the wing and carcass were significantly correlated. Residues were relatively low in oldsquaw foods from Lake Michigan; concentration factors between the food and the ducks varied between 1X and 22X, depending on the date and compound. Organochlorinated residues were lower in Arctic than in Lake Michigan food samples. DDE in paired male and female oldsquaws was highly correlated, as was DDE in females and clutches. Eggshell thickness had declined 4.5% compared with eggs collected before 1947. Residues were higher in oldsquaws wintering on the Great Lakes and lowest in oldsquaws from coastal areas.

Age Factors↗

[Dieldrin, aldrin, endrin, isodrin, endosulfan 1 and 2 on fish in the Gulf of Gdańsk].

The residues of dieldrin, aldrin, endrin, isodrin, endosulfan 1 and 2 has been determined in a several species of fish caught in the Gulf of Gdańsk in 1992. The method of measurement was capillary gas chromatograph and low resolution mass spectrometry (HRGC/LRMS) after a nondestructive extraction and clean-up step with a further fractionation of the extract on Florisil column. Apart from dieldrin no other cyclodiene pesticides studied were found in fishes in detectable amounts, and for dieldrin concentrations ranged from 0.84 to 6.6 ng/g wet weight.

Animals↗