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Biomedical subjects

A M Cook

Publications and source records attributed to A M Cook.

At least 91 records · Page 5Linked to original sources
PubMed1985

Ring cleavage and degradative pathway of cyanuric acid in bacteria.

The degradative pathway of cyanuric acid [1,3,5-triazine-2,4,6(1H,3H,5H)-trione] was examined in Pseudomonas sp. strain D. The bacterium grew with cyanuric acid, biuret, urea or NH4+ as sole source of nitrogen, and each substrate was entirely metabolized concomitantly with growth. Enzymes from strain D were separated by chromatography on DEAE-cellulose and three reactions were examined. Cyanuric acid (1 mol) was converted stoichiometrically into 1.0 mol of CO2 and 1.1 mol of biuret, which was conclusively identified. Biuret (1 mol) was converted stoichiometrically into 1.1 mol of NH4+, about 1 mol of CO2 and 1.0 mol of urea, which was conclusively identified. Urea (1 mol) was converted into 1.9 mol of NH4+ and 1.0 mol of CO2. The reactions proceeded under aerobic or anoxic conditions and were presumed to be hydrolytic. Data indicate that the same pathway occurred in another pseudomonad and a strain of Klebsiella pneumoniae.

Ammonia↗
PubMed1984

Bacterial degradation of N-cyclopropylmelamine. The steps to ring cleavage.

The s-triazine cyclopropylmelamine (N-cyclopropyl-1,3,5-triazine-2,4,6-triamine) was degraded to about 6 mol of NH4+/mol of substrate by a mixture of two bacteria (strains A and D, both Pseudomonas spp.) Only strain A grew with cyclopropylmelamine as sole and limiting source of nitrogen. The organism obtained 2 mol of nitrogen/mol of substrate and excreted a product that was identified as cyclopropylammelide [6-cyclopropylamino-1,3,5-triazine-2,4(1 H,3 H)-dione]. Proteins in extracts from strain A were separated on a Sephadex G-200 column. Cyclopropylmelamine was found to be deaminated in two separable steps to cyclopropylammelide via cyclopropylammeline [4-amino-6-cyclopropylamino-1,3,5-triazine-2(1 H)-one], which was identified. Strain D could not utilize cyclopropylmelamine or cyclopropylammeline, but could utilize cyclopropylammelide (or homologue) as sole and limiting source of nitrogen and obtain about 4 mol of nitrogen/mol of substrate. Proteins in cell extracts from strain D were separated on a DEAE-cellulose column. Alkylammelides were degraded quantitatively by one enzyme fraction to 1 mol of cyanuric acid plus 1 mol of alkylamine/mol of substrate. The specific activities of enzymes in extracts of the two strains were as high as the activities observed during growth. The three activities studied in the two strains were all active under aerobic and oxygen-free conditions. The reactions appear to be hydrolytic, yielding 2 mol of NH4+ plus 1 mol of cyclopropylamine and 1 mol of cyanuric acid/mol of substrate.

Chemical Phenomena↗
PubMed1984

2-Chloro-4-amino-1,3,5-triazine-6(5H)-one: a new intermediate in the biodegradation of chlorinated s-triazines.

Pseudomonas sp. strain A grew with 2-chloro-1,3,5-triazine-4,6-diamine as the sole and growth-limiting source of nitrogen. The substrate was utilized quantitatively and concomitantly with growth and with excretion of a product which was identified as 2-chloro-4-amino-1,3,5-triazine-6(5H)-one. The reaction yielded 1 mol of organic product and 1 mol of NH4+ per mol of substrate.

Biodegradation, Environmental↗
PubMed1983

Qualitative analysis of waste-water from ametryne production.

s-Triazines in waste-water from the synthesis of ametryne (2-(ethylamino)-4-[(l-methylethyl) amino]-6-(methylthio)-1,3,5-triazine) were tentatively identified co-chromatographically by HPLC and by UV-spectra. Alkylated s-triazines (e.g. hydroxyametryne, 4-(ethylamino)-6-(methylthio)-1,3,5-triazine-2(1H)-one, and N-ethylammelide) were isolated by preparative chromatography on a reversed phase support, and were identified by mass spectrometry. Putative cyanuric acid was desalted on activated charcoal and its identity confirmed as the silylated derivative by GLC.

Herbicides↗
PubMed1982

The degradative pathway of the s-triazine melamine. The steps to ring cleavage.

1. The degradative pathway of melamine (1,3,5-triazine-2,4,6-triamine) was examined in Pseudomonas sp. strain A. 2. The bacterium grew with melamine, ammeline, ammelide, cyanuric acid or NH+4 as sole source of nitrogen, and each substrate was entirely metabolized. Utilization of ammeline, ammelide, cyanuric acid or NH+4 was concomitant with growth. But with melamine as substrate, a transient intermediate was detected, which was identified as ammeline by three methods. 3. Enzymes from strain A were separated by chromatography on DEAE-cellulose, and four activities were examined. 4. Melamine was converted stoichiometrically into equimolar amounts of ammeline and NH+4. 5. Ammeline was converted stoichiometrically into equimolar amounts of ammelide and NH+4; ammelide was identified by four methods. 6. Ammelide was converted stoichiometrically into equimolar amounts of cyanuric acid and NH+4; cyanuric acid was identified by four methods. 7. Cyanuric acid was converted by an enzyme preparation into an unidentified product with negligible release of NH+4. 8. The specific activities of the degradative enzymes (greater than or equal to 0.3 mkat/kg of protein) were high enough to explain the growth rate of the organism. 9. The bacterium converted 0.4 mM-melamine anaerobically into 2.3 mM-NH+4. 10. Two other pseudomonads and two strains of Klebsiella pneumoniae were also examined, with similar results. 11. The degradative pathway of melamine appears to be hydrolytic, and proceeds by three successive deaminations to cyanuric acid, which is further metabolized.

Chemical Phenomena↗
PubMed1982

Multiple "cold" areas demonstrated on bone scintigraphy in a patient with neuroblastoma.

A "cold" or photopenic defect on bone scintigraphy is a well recognized phenomenon and has been described in several conditions affecting bone. An unusual case of multiple "cold" defects in a patient with stage IV neuroblastoma is presented. A follow-up scan with the patient in clinical remission shows resolution of these "cold" defects. The patient subsequently relapsed and again multiple new "cold" defects were noted on bone scintigraphy. The possible etiology of "cold" defects is discussed.

Bone Marrow↗
PubMed1980

Assessing non-oral clients for assistive communication devices.

As the number of commercially available communication aids increases, determining an appropriate device for a particular client becomes more difficult. The development of systematic assessment procedures on which to base device recommendations has therefore become an important research problem. This report presents a set of assessment procedures developed by the authors in the Assistive Device Center at California State University-Sacramento. These procedures and their use in determining a communication device recommendation are ilustrated through a description of two case studies.

Adult↗
PubMed1979

Phosphate and soil binding: factors limiting bacterial degradation of ionic phosphorus-containing pesticide metabolites.

Soils that had a high binding capacity for inorganic orthophosphate (Pi) had reduced capacities to bind ionic alkyl phosphorus compounds. Only ionic methylphosphonate (MPn) and ionic phenylphosphonate exhibited moderate binding. Pseudomonas testosteroni used either MPn or Pi as a sole phosphorus source and exhibited diauxic utilization of MPn and Pi. The utilization of MPn was suppressed in the presence of Pi. This suppression was abolished by a Pi-binding soil. The soil did not have a significant effect on the maximum rate of degradation of either MPn or the poorly bound ionic O-isopropyl methylphosphonate, whereas the amount of MPn (but not the amount of O-isopropyl methylphosphonate) metabolized was reduced in the presence of soil

Biodegradation, Environmental↗
PubMed1978

Phosphorus-containing pesticide breakdown products: quantitative utilization as phosphorus sources by bacteria.

Bacteria were isolated that could utilize representatives of the following ionic phosphorus-containing breakdown products of organophosphorus pesticides as sole phosphorus sources: dialkyl phosphates, dialkyl phosphorothioates, dialkyl phosphorodithioates, alkyl arylphosphonates, alkyl arylphosphonothioates, and alkyl alkylphosphonates. Utilization of each organophosphorus compound, which was complete for 7 of 12 compounds studied, was confirmed by determination of protein yield from the amount of phosphorus source consumed. This is the first report of the utilization of an ionic dialkyl thiophosphate or dithiophosphate by microorganisms.

Bacteria↗
PubMed1978

Phosphonate utilization by bacteria.

Bacteria able to use at least one of 13 ionic alkylphosphonates of O-alkyl or O,O-dialkyl alkylphosphonates as phosphorus sources were isolated from sewage and soil. Four of these isolates used 2-aminoethylphosphonic acid (AEP) as a sole carbon, nitrogen, and phosphorus source. None of the other phosphonates served as a carbon source for the organisms. One isolate, identified as Pseudomonas putida, grew with AEP as its sole carbon, nitrogen, and phosphorus source and released nearly all of the organic phosphorus as orthophosphate and 72% of the AEP nitrogen as ammonium. This is the first demonstration of utilization of a phosphonoalkyl moiety as a sole carbon source. Cell-free extracts of P. putida contained an inducible enzyme system that required pyruvate and pyridoxal phosphate to release orthophosphate from AEP; acetaldehyde was tentatively identified as a second product. Phosphite inhibited the enzyme system.

Aminoethylphosphonic Acid↗