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)

Simple and flexible methods have been designed for the determination of pentachlorophenol in animal tissue, blood plasma, urine, and aerosol. The isolation of the pesticide is achieved through its extraction with benzene or hexane after acidification, derivatization, and its subsequent purification through florosil columns. A brief describption of the sampling methods is included. The described procedures are especially suited for exposure experiments where different types of samples with a large variety of PCP concentrations are encountered.
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PMID:A study of the inhalation of pentachlorophenol by rats. Part I. A method for the determination of pentachlorophenol in rat plasma, urine and tissue and in aerosol samples. 127 91

DNA in macro- and micronuclei of Tetrahymena pyriformis treated with linear alkyl benzene sulfonate (LAS) and sodium pentachlorophenate (PCP-Na) were determined by microspectrophotometry. The effects on rate of formation of macronuclear DNA extrusion bodies were also studied. We found DNA content of micronuclei in 0.14 ppm LAS and 0.9 ppb PCP-Na was lower than in that of the control, and LAS was able to increase the formation rate of macronuclear DNA extrusion bodies (the formation rate was 54% in 11.3 ppm LAS and 25.6% in 16.7 ppm dichromate). We concluded that 0.14 ppm LAS (below the maximum acceptable toxicant concentration) was genotoxic, whereas 0.014 ppm LAS was not. Dichromate 0.05 ppm and 0.9 ppb PCP-Na, equal to and below the maximum acceptable toxicant concentration, respectively, were potentially genotoxic.
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PMID:Genotoxic effects of linear alkyl benzene sulfonate, sodium pentachlorophenate and dichromate on Tetrahymena pyriformis. 132 23

This review focuses of industrial chemicals that research has indicated may adversely affect human male reproductive capacity. The study of male reproductive toxicity is impeded by a dearth of clinical endpoints. Males lack an obvious and easily measurable reproductive cycle, and the primary clinical indicator, semen analysis, offers unsure clues to reproductive performance. However, progress is being made in developing and evaluating tests to identify chemical hazards and estimate human health risks. Agents with confirmed adverse effects of male reproduction include carbon disulfide, dibromocklopropane, lead, and oral contraceptives. Agents with inconclusive effects include anesthetic gases, arsenic, benzene, boron, cadmium, carbaryl, chlordecone, chloroprene, DNT and TDA, ethylene dibromide, manganese, mercury, pesticides, PCP, radiation ionizing and nonionizing, solvents, dioxin, and vinyl chloride. Finally, agents with no observed adverse effects include epichlorohydrin, glycerine, benzoic acid, and polybrominated biphenyls. The literature suggests a need for further research in the following areas: 1) chemicals that are reactive and capable of covalent interactions in biological systems, 2) chemicals defined as mutagens and/or carcinogens in short-term laboratory tests, 3) chemicals demonstrated to cause aneuploidy or other chromosomal aberrations, 4) chemicals that affect sperm motility in vitro, 5) chemicals that share hormonal activity or affect hormone action, and 6) chemicals that act directly or indirectly to affect the hypothalamo-pituitary-gonadal axis.
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PMID:Occupational exposures associated with male reproductive dysfunction. 240 59

The purpose of the present experiments was to evaluate the effects of eliminating or varying the size of the cycloalkyl ring of phencyclidine (PCP) from 3 to 8 carbons while leaving the composition of the benzene and piperidine rings unaltered. Compounds were evaluated for their effectiveness in producing PCP-like discriminative stimuli and changes in pupil diameter in the rat and impaired motor performance on the Rotarod in the mouse. All modifications of the cycloalkyl ring of PCP significantly reduced the relative potencies of the cycloalkyl analogs, shortened their duration of action and also modified their spectra of action, including their effectiveness in producing PCP-like discriminative stimuli and miosis in the rat as well as ataxia in the mouse. The present results demonstrate that the cyclohexyl moiety of PCP is an absolute requirement for producing a full PCP-like spectrum of activity.
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PMID:Effects of cycloalkyl ring analogs of phencyclidine on behavior in rodents. 682 58

(PCP)Ir(H)2 (PCP = eta3-1,3-C6H3(CH2PR2)2) complexes are highly effective catalysts for the dehydrogenation of alkanes; in particular, they are the first efficient molecular catalysts for alkane dehydrogenation that do not require a sacrificial hydrogen acceptor. Using density functional theory/effective core potential methods, we have examined C-H bond cleavage in alkanes and arenes by both (PCP)Ir and (PCP)Ir(H)2. C-H addition to the dihydride is accompanied by loss of H2; both associative and dissociative pathways for this exchange reaction have been examined. The energetic barrier (deltaE(is not equal)) for associative displacement of H2 by benzene is much lower than the barrier for a dissociative pathway involving initial loss of H2; however, the pathways have very comparable free energy barriers (deltaG(is not equal)). Extrapolation to the higher temperatures, bulkier phosphine ligands, and the alkane substrates used experimentally leads to the conclusion that the pathway for the "acceptorless" dehydrogenation of alkanes is dissociative. For hydrocarbon/hydrocarbon exchanges, which are required for transfer-dehydrogenation, dissociative pathways are calculated to be much more favorable than associative pathways. We emphasize that it is the free energy, not just the internal energy or enthalpy, that must be considered for elementary steps that show changes in molecularity.
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PMID:DFT/ECP study of C-H activation by (PCP)Ir and (PCP)Ir(H)2(PCP=eta3-1,3-C6H3(CH2PR2)2). Enthalpies and free energies of associative and dissociative pathways. 1120 83

This paper presents the system-level responses of experimental lake ecosystems to three chemical stresses (acidification, copper and pesticide contamination) using exergy and structural exergy as ecological indicators. The results indicate that the doses or toxicity of the three chemical stressors contributed to changes in both exergy and structural exergy. Remarkable changes in exergy and structural exergy occurred under acidic conditions and in the presence of Dursban, 24D-DMA, permethrin, bifenthrin, Carbaryl, TCP, PCP, trichlorethylene, benzene, and high doses of Cu, oil, and hexazinone. This seemed to indicate that the subject ecosystems were seriously contaminated by these chemical stressors. For low doses of Cu, oil, atrazine, HCBP, and hexazinone, exergy and structural exergy were either unchanged or only slightly changed, suggesting that the lake ecosystems were not significantly impacted by these chemical stressors. Discussion of the relationships between ecosystem-level changes and structural and functional changes in stressed lake ecosystems indicates that the above-mentioned ecosystem-level changes were in accordance with the changes in structure and function. The observed changes in exergy and structural exergy were also consistent with Odum's predictions of shortened food chains, reduced resource use efficiency, poor stability, low information, and high entropy in stressed aquatic ecosystems. The findings lead the authors to conclude that it is feasible for exergy and structural exergy to serve as ecological indicators when characterizing the system-level responses of experimental lake ecosystems to chemical stress. These results for experimental lake ecosystems would be extrapolated to actual lakes.
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PMID:System-level responses of lake ecosystems to chemical stresses using exergy and structural exergy as ecological indicators. 1182 73

The cationic PNP-Ir(I)(cyclooctene) complex 1 (PNP = 2,6-bis-(di-tert-butyl phosphino methyl)pyridine) reacts with benzene at 25 degrees C to quantitatively yield the crystallographically characterized, square pyramidal, iridium phenyl hydride complex cis-(PNP)Ir(Ph)(H), 2, in which the hydride is trans to the vacant coordination site. The cationic complex 2 is stable to heating at 100 degrees C, in sharp contrast to the previously reported unstable neutral, isoelectronic (PCP)Ir(H)(Ph) (PCP = eta(3)-2,6-((t)()Bu(2)PCH(2))(2)C(6)H(3)). Heating of 2 at 50 degrees C with other arenes results in arene exchange. Complex 1 activates C-H bonds of chloro- and bromobenzene with no C-halide oxidative addition being observed. Selective ortho C-H activation takes place, the process being directed by halogen coordination and being thermodynamically and kinetically favorable. The meta- and para-C-H activation products are formed at a slower rate than the ortho isomer and are converted to it. NMR data and an X-ray crystallographic study of the ortho-activated chlorobenzene complex, which was obtained as the only product upon heating of 1 with chlorobenzene at 60 degrees C, show that the chloro substituent is coordinated to the metal center.
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PMID:Selective ortho C-h activation of haloarenes by an Ir(I) system. 1269 82

PCP ligand (1,3-bis-[(diisopropyl-phosphanyl)-methyl]-benzene), and PCN ligand ([3-[(di-tert-butyl-phosphanyl)-methyl]-benzyl]-diethyl-amine) based rhodium dinitrogen complexes (1 and 2, respectively) react with phenyl diazomethane at room temperature to give PCP and PCN-Rh carbene complexes (3 and 5, respectively). At low temperature (-70 degrees C), PCP and PCN phenyl diazomethane complexes (4 and 6, respectively) are formed upon addition of phenyl diazomethane to 1 and 2. In these complexes, the diazo moiety is eta(1) coordinated through the terminal nitrogen atom. Decomposition of complexes 4 and 6 at low temperatures leads only to a relatively small amount of the corresponding carbene complexes, the major products of decomposition being the dinitrogen complexes 1 and 2 and stilbene. This and competition experiments (decomposition of 6 in the presence of 1) suggests that phenyl diazomethane can dissociate under the reaction conditions and attack the metal center through the diazo carbon producing a eta(1)-C bound diazo complex. Computational studies based on a two-layer ONIOM model, using the mPW1K exchange-correlation functional and a variety of basis sets for PCP based systems, provide mechanistic insight. In the case of less bulky PCP ligand bearing H-substituents on the phosphines, a variety of mechanisms are possible, including both dissociative and nondissociative pathways. On the other hand, in the case of i-Pr substituents, the eta(1)-C bound diazo complex appears to be a critical intermediate for carbene complex formation, in good agreement with the experimental results. Our results and the analysis of reported data suggest that the outcome of the reaction between a diazoalkane and a late transition metal complex can be anticipated considering steric requirements relevant to eta(1)-C diazo complex formation.
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PMID:Metallacarbenes from diazoalkanes: an experimental and computational study of the reaction mechanism. 1278 93

Studies are described that reveal the steps of the anti-Markovnikov hydroamination of vinylarenes with alkylamines catalyzed by Ru(COD)(2-methylallyl)2, bis(diphenylphosphino)pentane, and TfOH. Treatment of the catalyst components with an excess of styrene under the catalytic reaction conditions afforded a new ruthenium eta6-styrene complex with an ancillary tridentate PCP ligand. This ruthenium complex was active as catalyst for the hydroamination of styrene with morpholine to give the anti-Markovnikov adduct as a single regioisomer in high yield. Studies of the reactivity of the eta6-styrene complex revealed two reactions that comprise a catalytic cycle for anti-Markovnikov hydroamination: nucleophilic addition of morpholine to the ruthenium eta6-styrene complex to afford a ruthenium eta6-(2-aminoethyl)benzene complex and arene exchange of the ruthenium eta6-(2-aminoethyl)benzene complex with styrene to regenerate the ruthenium eta6-styrene complex. The addition of morpholine and the exchange of arene occurred with comparable rates. These results strongly suggest that the ruthenium-catalyzed anti-Markovnikov addition of alkylamines to vinylarenes occurs by a new reaction mechanism for hydroamination involving nucleophilic attack on the eta6-vinylarene complex and exchange of the aminoalkylarene complex product with free vinylarene. This mechanism is a rare example of catalytic chemistry through pi-arene complexes. These mechanistic data were used to select derivatives of the DPPP ligand that improve the rates of the catalytic process.
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PMID:Mechanistic Studies of Ruthenium-Catalyzed Anti-Markovnikov Hydroamination of Vinylarenes: Intermediates and Evidence for Catalysis through pi-Arene Complexes. 1583 51

Electrochemical reduction with electrochemically generated naphthalene radical anion in N,N-dimethylformamide was applied to the dechlorination of five representative POPs, namely HCB, lindane, DDT, PCP and aldrin. Rapid and complete dechlorination was possible for lindane and DDT to give nearly quantitative yields of benzene and 1,1-diphenylethane, respectively. HCB was reduced through complex reaction pathways to yield unknown products. Dechlorination of PCP and aldrin beyond dichlorinated compounds was difficult because of their very negative reduction potential. The reaction pathways for each dechlorination were proposed with the identification of intermediates.
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PMID:Dechlorination of polychlorinated organic compounds by electrochemical reduction with naphthalene radical anion as mediator. 1587 91


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