Gene/Protein Disease Symptom Drug Enzyme Compound
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Query: EC:3.4.16.2 (PCP)
 3,761 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

The effects of phencyclidine (PCP) on the behavior of rats responding to a fixed-interval 1 min schedule of water delivery were determined before, during, and after a period of daily PCP injections. The effects of acute PCP on overall response rate were biphasic: low doses increased and high doses decreased rates. In addition, PCP produced a dose-related decrease in quarter-life and high doses of PCP decreased the number of reinforcers delivered. During the daily injection regimen roughly a two-fold tolerance developed to the effects of 8.0 mg/kg PCP on response rate in animals receiving either presession or post-session injections of this dose, emphasizing the predominance of pharmacological variables in PCP tolerance. However, slight differences between these groups in tolerance development and in the rate of tolerance loss demonstrate that behavioral variables can influence tolerance to the behavioral effects of PCP.
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PMID:Tolerance to the behavioral effects of phencyclidine: the importance of behavioral and pharmacological variables. 11 26

The distribution and metabolic fate of several rice paddy pesticides were evaluated in a modified model ecosystem. Among the three BHC isomers, beta-isomer was the most stable and bioconcentrated in all of the organisms. Alpha- and gamma-isomers were moderately persistent and degraded to some extent during the 33 day period. Disulfoton was relatively persistent due to the transformation to its oxidation products. Pyridaphenthion was fairly biodegradable. N-Phenyl maleic hydrazide derived from the hydrolysis of pyridaphenthion was not detected in the organisms though it was found in the aquarium water after 33 days. Cartap and edifenphos were considerably biodegradable, and the ratio of the conversion to water soluble metabolites was very high. There was a distinct difference in the persistence of Kitazin P and edifenphos in the aquarium water. It appeared that the hydrolysis rate of the pesticides affected their fate in the organisms. PCP appeared to be moderately biodegradable. CNP was considerably stable and stored in the organisms though the concentration in the aquarium water was relatively low. The persistence and distribution of the pesticides in the model ecosystem were dependent on their chemical structures. In spite of the limitation derived from short experimental period, the model ecosystem may be applicable for predicting the environmental fate of pesticides.
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PMID:Environmental fate of rice paddy pesticides in a model ecosystem. 43 58

Chemical and serological investigations were carried out on lipopolysaccharides of 4 Salmonella S-forms and of 1 SR-mutant, extracted from bacteria at different ages of culture (early exponential to stationary growth phase). The results show that the fatty acid composition of Lipid A (lauric-, myristic-, palmitic-, and beta-hydroxy-myristic acids) does not undergo any significant change during the growth of the cultures. However, there are differences in the molar ratios of the fatty acids from strain to strain. In all phases of growth Lipid A is substituted by basaloligosaccharide, to the same extent, as can be seen from the constant ratios of beta-hydroxy-myristic acid: heptose. Serological experiments (haemagglutination inhibition tests, absorption of antibodies by LPS-coated erythrocytes) showed that in no case the basaloligosaccharide is completely substituted by O-specific chains and that basaloligosaccharide exhibits free R-antigen structures which are mainly of chemotypes Ra, Rb and Rc, for the SR-mutant only of types Ra and Rb. There is no demonstrable dependence upon the phases of growth. In the O-specific polysaccharide chains the sugars of the main chain and the side bound dideoxy sugars (abequose and tyvelose) show a constant 1:1 molar ratio in all phases. In the case of S. typhimurium, antigen factors 1, 4 and 12(2), the biosynthesis of which is controlled by modifying oaf genes and/or by a lysogenic phage, are of a somewhat weaker expression in the exponential phase than in the latter phases of growth. In the SR-mutant, lipopolysaccarides with (low) serological O1 and O12(2) activity are only extractable by the phenol/water method, but not by the PCP method. In three out of four S-forms, changes occur in the length of the O-specific polysaccharide chains, whereas the number of repeating units of the fourth strain remains almost unchanged. The lipopolysaccharides of the SR-mutant contain in all phases of growth about one repeating unit. In all strains the covering of the cell surface by lipopolysaccharide molecules changes during the course of growth, as can be seen by comparing the relative cell surface and the content of Lipid A fatty acids of the bacteria. Lipid A synthesis in the 4 S-forms is reduced in the exponential phase and/or in the phase of delayed growth acceleration. The extent of biosynthesis of the carbohydrate moiety of lipopolysaccharides is independent of that of Lipoid A. In the SR-mutant, Lipoid A and Polysaccharide are formed in increased amounts in the exponential growth phase.
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PMID:[Chemical and serological characterization of Salmonella lipopolysaccharides from different phases of growth (author's transl)]. 76 1

The results of this investigation have shown that PCP persisted in leaf litter and sediments for at least seventeen months following contamination. This persistence provides a potential for continuous contamination of the water column and biological magnification via detritus- and benthic-feeding organisms. An investigation of these factors is presently underway.
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PMID:Pentachlorophenol distribution in a fresh water ecosystem. 89 Jan 62

A commercially available bacterial toxicity monitor ("Toxiguard", BTG Anlagentechnik, Bochum, Germany) was tested for continuous river monitoring. Operating with biofilms, this system shall detect toxic substances in the water. River water passes through two bioreactors forming a biofilm of characteristic river bacteria. The indicating parameter of the biomonitor is the respiration rate of this bacterial biofilter. The remaining oxygen content in the effluent from the biofilter is measured continuously by an oxygen electrode. This value is related to the dissolved oxygen (DO) of the river water measured in a by-pass. In presence of inhibitory substances the DO content in the biofilter increases because of the reduced respiration activity of the bacteria. The addition of nutrients may lead to an increase of biomass and of respiration activity. This results in an increasing oxygen difference between DO contents in the biofilter influent and effluent. Therefore, the degree of poisoning is better perceptible. Moreover each nutrient causes a distinct biofilm with a specific sensitivity against chemicals. This effect will be shown for Sodium-Pentachlorophenolate (Na-PCP).
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PMID:[Use of bioreactors for continuous water monitoring]. 130 95

The effects of injection of various purinoceptor agonists into the hypothalamic paraventricular nucleus in water-loaded and ethanol-anesthetized rats were investigated. Adenosine triphosphate (ATP), beta,gamma-methyleneadenosine 5'-triphosphate (AMP-PCP) and beta,gamma-imidoadenosine 5'-triphosphate (AMP-PNP) potently decreased the outflow of urine in a time- and dose-dependent manner. The ED50 values were approx 70 and 37 nmol for ATP and AMP-PCP, respectively. Adenosine diphosphate (ADP), AMP and adenosine reduced the outflow of urine much less than ATP. Adenosine triphosphate induced concomitant increases in the osmotic pressure of the urine and in the level of arginine-vasopressin (AVP) in plasma. The antidiuretic effect of ATP was blocked by prior injection of quinidine (a P2-purinoceptor antagonist) into the paraventricular nucleus, but not by the prior injection of theophylline (a P1-purinoceptor antagonist). The effect of ATP was also blocked by intravenous injection of an AVP(V1V2)-receptor antagonist, d(CH2)5-D-Tyr(Et)VAVP. The results suggest that ATP injected into the paraventricular nucleus may stimulate a purinoceptor, releasing AVP and inducing the antidiuretic effect through renal AVP(V2) receptors.
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PMID:Antidiuretic effects of purinoceptor agonists injected into the hypothalamic paraventricular nucleus of water-loaded, ethanol-anesthetized rats. 140 98

The effects of buprenorphine on behavior reinforced by smoked cocaine base and orally delivered phencyclidine (PCP), ethanol and saccharin were compared. There were six groups of four to five rhesus monkeys. Group 1 contained four monkeys that had been trained to smoke cocaine base under progressive ratio (PR) or fixed ratio (FR) schedules. Up to eight smoke deliveries (2 mg/kg) were available during daily 3-hr sessions. Each delivery was separated by a 15-min timeout. The remaining groups received concurrent access to different combinations of orally delivered liquids as follows: group 2, PCP (0.25 mg/ml) and water; group 3, saccharin (0.03% w/v) and water; group 4, PCP and saccharin; group 5, ethanol (8% w/v) and water; and group 6, ethanol and PCP. Saline or buprenorphine (0.003, 0.012, 0.05, 0.2 and 0.8 mg/kg) injections were given i.m. 30 min before each session for 5 consecutive days. Buprenorphine produced a dose-dependent reduction in behavior maintained by PCP, ethanol or saccharin in all of the six groups. In group 1, the suppressant effects of buprenorphine on cocaine base smoking were greater in the two monkeys that responded under FR 5 schedules than in the two that responded under PR schedules. When PCP and saccharin were concurrently available (group 4), buprenorphine had a greater suppressant effect on PCP than when water was concurrently present (group 2). Buprenorphine produced nearly a complete suppression in saccharin-maintained responding at doses of 0.012 mg/kg and higher in groups 3 and 4. Buprenorphine reduced ethanol deliveries to about 50% at doses of 0.012 mg/kg and higher in group 5. When PCP and ethanol were concurrently available (group 6), buprenorphine had an effect on PCP and ethanol that was similar to that found when the drugs were available concurrently with water. These results suggest that buprenorphine suppresses behavior maintained by several drug and nondrug substances, and it further suppresses PCP-maintained behavior that is already reduced by a nondrug alternative reinforcer.
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PMID:Buprenorphine's effects on self-administration of smoked cocaine base and orally delivered phencyclidine, ethanol and saccharin in rhesus monkeys. 156 Mar 73

White rot fungi such as P. chrysosporium degrade the nonrepeating, nonstereoselective, insoluble polymer lignin under conditions of nutrient limitation. The attack on lignin principally involves extracellular peroxidases (ligninases) and hydrogen peroxide. Hydroxyl radicals may also make a significant contribution. The ligninolytic system lends itself to the degradation of xenobiotics, since these often have limited solubility in water and are not readily available in soil to intracellular metabolism. A nonspecific attack should proceed at a rate independent of the target's concentration and the fungal system would be expected to remediate soil contaminated with a mixture of compounds. This contrasts with the need for induction and problems with simultaneous metabolism encountered with bacterial inoculation. The P. chrysosporium system has been found active against such diverse substrates as DDT, lindane, PCBs, TNT and crystal violet, with substantial mineralization in many cases. Some like biphenyl and triphenylmethane dyes are structurally related to lignin substructures while others bear groups such as nitro (TNT) or halogen (PCP) that are absent from the natural polymer. The fate of transformed targets varies: pentachlorophenol is incorporated into soil organic matter as a result of fungal ligninase action, whereas highly lipophilic Aroclor PCBs are converted to water-soluble metabolites. Normally less toxic intermediates are generated: for example, with benzo[a]pyrene, mutagenic arene oxides do not appear in the white rot fungal system. In certain cases, purified ligninases were also active in degrading pollutants such as PCP, benzo[a]pyrene or triphenylmethane dyes. Methods of optimizing ligninase activity in fungal reactors have been described, such as the addition of surfactants and veratryl alcohol to the medium. It remains to be seen how molecular biology can provide further advances in maximizing the bioremediating activity of white rot fungi applied to contaminated soil.
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PMID:Degradation of xenobiotics by white rot fungi. 177 Dec 73

Six rhesus monkeys self-administered orally-delivered phencyclidine (PCP) and water under concurrent fixed-ratio (FR) 8 schedules. Liquids were available during three 6.5-h periods daily preceded by 1-h components when food was available under an FR 64 (lever press) schedule. After 10 days of stable behavior, water was substituted for PCP for 8 days. PCP was subsequently reinstated, and this PCP withdrawal sequence was repeated using different food FR values (64, 128, 256, 512 and 1024). Each time the food FR was changed behavior was allowed to stabilize for at least 10 days. Under all FR values food-maintained responding decreased markedly during PCP withdrawal, with a gradual recovery over the next 8 days. As the FR value increased from 64 to 1024 there was a parallel shift downward in food-maintained performance. When PCP was reinstated, food-reinforced responding generally returned to baseline rates during the first few days. In a second experiment monkeys were tested for PCP withdrawal effects under relatively food deprived or food satiated conditions under both an FR 512 and 1024 schedule of food delivery. The results showed that the decrease in food-maintained responding during withdrawal was inversely related to the total amount of food consumed during the control period. The results of these experiments indicate that manipulation of both the response requirements for food (FR) and the total amount of food available (food deprivation/satiation) alters the magnitude of response disruptions during PCP withdrawal.
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PMID:Effects of food FR and food deprivation on disruptions in food-maintained performance of monkeys during phencyclidine withdrawal. 187 58

Organochlorine residues (OCR)2 are poorly soluble in water and are transported in the organism bound by the blood components. The distribution among blood fractions (cells/plasma, lipoproteins/rest of plasma proteins) were variable depending on the residue (HCB, p p'-DDE, HCH, Aroclor 1260, PCP) and on the species (rat, man). Differences were not found between in vivo (after oral single dosing) and in vitro (blood incubation) experiments. Results indicated a high affinity of organochlorine residues for lipoproteins; however, binding to blood carriers was very weak as demonstrated by the rapid release of residues by elution through a reverse phase column. The effects of residue binding to blood components on the distribution kinetics to tissues are discussed.
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PMID:Transport of organochlorine residues in the rat and human blood. 199 12


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