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.     

Metabolism of Melamine by Klebsiella terragena

Experiments were conducted to determine the pathway of melamine metabolism by Klebsiella terragena (strain DRS-1) and the effect of added NH(inf4)(sup+) on the rates and extent of melamine metabolism. In the absence of added NH(inf4)(sup+), 1 mM melamine was metabolized concomitantly with growth. Ammeline, ammelide, cyanuric acid, and NH(inf4)(sup+) accumulated transiently in the culture medium to maximal concentrations of 0.012 mM, 0.39 mM, trace levels, and 0.61 mM, respectively. In separate incubations, in which cells were grown on either ammeline or ammelide (in the absence of NH(inf4)(sup+)), ammeline was metabolized without a lag while ammelide metabolism was observed only after 3 h. In the presence of 6 mM added NH(inf4)(sup+) (enriched with 5% (sup15)N), ammeline, ammelide, and cyanuric acid accumulated transiently to maximal concentrations of 0.002 mM, 0.47 mM, and trace levels, respectively, indicating that the added NH(inf4)(sup+) had little effect on the relative rates of triazine metabolism. These data suggest that the primary mode of melamine metabolism by K. terragena is hydrolytic, resulting in successive deaminations of the triazine ring. Use of (sup15)N-enriched NH(inf4)(sup+) allowed estimates of rates of triazine-N mineralization and assimilation of NH(inf4)(sup+)-N versus triazine-N into biomass. A decrease in the percent (sup15)N in the external NH(inf4)(sup+) pool, in conjunction with the accumulation of ammelide and/or triazine-derived NH(inf4)(sup+) in the culture medium, suggests that the initial reactions in the melamine metabolic pathway may occur outside the cytoplasmic membrane.     

Biodegradation of melamine and its hydroxy derivatives by a bacterial consortium containing a novel Nocardioides species

Melamine has recently been recognized as a food contaminant with adverse human health effects. Melamine contamination in some crops arises from soil and water pollution from various causes. To remove melamine from the polluted environment, a novel bacterium, Nocardioides sp. strain ATD6, capable of degrading melamine was enriched and isolated from a paddy soil sample. The enrichment culture was performed by the soil-charcoal perfusion method in the presence of triazine-degrading bacteria previously obtained. Strain ATD6 degraded melamine and accumulated cyanuric acid and ammonium, via the intermediates ammeline and ammelide. No gene known to encode for triazine-degrading enzymes was detected in strain ATD6. A mixed culture of strain ATD6 and a simazine-degrading Methyloversatilis sp. strain CDB21 completely degraded melamine, but the degradation rate of cyanuric acid was slow. The degradation of melamine and its catabolites by the mixed culture was greatly enhanced by including Bradyrhizobium japonicum strain CSB1 in the inoculum and adding ethanol to the culture medium. The melamine-degrading consortium consisting of strains ATD6, CDB21, and CSB1 appears to be potentially safer than other known melamine-degrading bacteria for the bioremediation of farmland and other contaminated sites, as no known pathogens were included in the consortium.     

Cloning and analysis of s-triazine catabolic genes from Pseudomonas sp. strain NRRLB-12227.

Pseudomonas sp. strain NRRLB-12227 degrades the s-triazine melamine by a six-step pathway which allows it to use melamine and pathway intermediates as nitrogen sources. With the plasmid pLG221, mutants defective in five of the six steps of the pathway were generated. Tn5-containing-EcoRI fragments from these mutants were cloned and identified by selection for Tn5-encoded kanamycin resistance in transformants. A restriction fragment from ammelide-negative mutant RE411 was used as a probe in colony hybridization experiments to identify cloned wild-type s-triazine catabolic genes encoding ammeline aminohydrolase, ammelide aminohydrolase, and cyanuric acid amidohydrolase. These genes were cloned from total cellular DNA on several similar, but not identical, HindIII fragments, as well as on a PstI fragment and a BglII fragment. Restriction mapping and Southern hybridization analyses of these cloned DNA fragments suggested that these s-triazine catabolic genes may be located on a transposable element, the ends of which are identical 2.2-kb insertion sequences.     

Characterization of a novel melamine-degrading bacterium isolated from a melamine-manufacturing factory in China

Melamine (2,4,6-triamino-1,3,5-triazine, C₃H₆N₆), belonging to the s-triazine family, is an anthropogenic and versatile raw material for a large number of consumer products and its extensive use has resulted in the contamination of melamine in the environment. A novel melamine-degrading bacterium strain CY1 was isolated from a melamine-manufacturing factory in China. The strain is phylogenetically different from the known melamine-degrading bacteria. Approximately, 94 % melamine (initial melamine concentration 4.0 mM, initial cell OD 0.05) was degraded in 10 days without the addition of additional carbon source. High-performance liquid chromatography showed the production of degradation intermediates including ammeline, ammelide, cyanuric acid, biuret, and urea. Kinetic simulation analysis indicated that transformation of urea into ammonia was the rate-limiting step for the degradation process. The melamine–cyanurate complex was formed due to self-assembly of melamine and cyanuric acid during the degradation. The tracking experiment using CY1 cells and ¹³C₃-melamine showed that the CY1 could mineralize s-triazine ring carbon to CO₂. The strain CY1 could also catalyze partial transformation of cyromazine, a cyclopropyl derivative of melamine, to 6-(cyclopropylamino)-[1,3,5]triazine-2,4-diol.     

Bacterial Ammeline Metabolism via Guanine Deaminase

Melamine toxicity in mammals has been attributed to the blockage of kidney tubules by insoluble complexes of melamine with cyanuric acid or uric acid. Bacteria metabolize melamine via three consecutive deamination reactions to generate cyanuric acid. The second deamination reaction, in which ammeline is the substrate, is common to many bacteria, but the genes and enzymes responsible have not been previously identified. Here, we combined bioinformatics and experimental data to identify guanine deaminase as the enzyme responsible for this biotransformation. The ammeline degradation phenotype was demonstrated in wild-type Escherichia coli and Pseudomonas strains, including E. coli K12 and Pseudomonas putida KT2440. Bioinformatics analysis of these and other genomes led to the hypothesis that the ammeline deaminating enzyme was guanine deaminase. An E. coli guanine deaminase deletion mutant was deficient in ammeline deaminase activity, supporting the role of guanine deaminase in this reaction. Two guanine deaminases from disparate sources (Bradyrhizobium japonicum USDA 110 and Homo sapiens) that had available X-ray structures were purified to homogeneity and shown to catalyze ammeline deamination at rates sufficient to support bacterial growth on ammeline as a sole nitrogen source. In silico models of guanine deaminase active sites showed that ammeline could bind to guanine deaminase in a similar orientation to guanine, with a favorable docking score. Other members of the amidohydrolase superfamily that are not guanine deaminases were assayed in vitro, and none had substantial ammeline deaminase activity. The present study indicated that widespread guanine deaminases have a promiscuous activity allowing them to catalyze a key reaction in the bacterial transformation of melamine to cyanuric acid and potentially contribute to the toxicity of melamine.Ammeline is an intermediate in the bacterial metabolism of melamine (Fig. ​(Fig.1).1). Melamine has become internationally recognized as a chemical adulterant in pet foods and infant formula that caused morbidity and mortality in pets and children (12). In pets, where more than 1,000 deaths have been attributed to melamine poisoning, the composition of the causal kidney precipitate was found to be a 1:1 complex of melamine-cyanuric acid (2, 25). In human babies, melamine-uric acid cocrystals have been identified (11). Feeding animals a mixture of melamine and cyanuric acid or a mixture of melamine, ammeline, ammelide, and cyanuric acid was found to produce acute kidney disease (5). Melamine and cyanuric acid are known to form a highly insoluble, hydrogen-bonded network (33) that can precipitate in the kidneys, causing kidney failure. Since bacterial metabolism of melamine generates cyanuric acid (6, 7, 14), it is possible that bacterial melamine metabolism could contribute to melamine toxicity in some cases.Open in a separate windowFIG. 1.The known metabolic pathway in bacteria for transforming melamine to cyanuric acid.Bacteria metabolize melamine by sequential deamination (4, 6, 7, 14, 30) to ammeline, ammelide, and cyanuric acid (Fig. ​(Fig.1).1). The genes and enzymes involved in the deamination of melamine and ammelide are known. Melamine deaminases (TriA and TrzA) have been purified and characterized (20, 28). The enzymes AtzC (34) and TrzC (7) were shown to be capable of ammelide deamination. Although ammeline deamination has been observed in a large number of microbial strains (37), the genes and enzymes involved in bacterial ammeline deamination have remained obscure. Many of the bacteria and fungi that were shown to deaminate ammeline did not deaminate melamine or ammelide (37), indicating that these ammeline deaminating enzymes have not evolved as a component of the melamine degradation pathway.Enzymes functioning in the metabolism of the s-triazine herbicide atrazine are related to some of the enzymes in the melamine pathway. TriA (melamine deaminase) is related to AtzA (28, 31) and TrzN (35), enzymes that catalyze the dechlorination of atrazine. AtzB, which catalyzes the second step in the atrazine metabolic pathway, was reported to also deaminate ammeline as a side reaction, but the rate of the reaction was not measured in that study (27).The enzymes involved in melamine and ammelide deamination, along with other enzymes acting on s-triazine herbicides, are all members of the amidohydrolase superfamily (32, 36). These enzymes typically contain one or two metal ions that are involved in activating water for nucleophilic displacement reactions. A significant number of amidohydrolase superfamily members catalyze deamination reactions with nitrogen heterocyclic ring substrates. In this context, we specifically analyzed the amidohydrolase enzymes in ammeline-metabolizing bacteria to identify the enzyme responsible for the activity. Molecular genetic, biochemical, and in silico data support the hypothesis that guanine deaminase functions as the principal ammeline deaminase activity of bacteria. This has implications for enzyme catalytic promiscuity and understanding the bacterial metabolism of melamine. The latter may be relevant to melamine toxicity in humans and animals.     

Enzymatic degradation of chlorodiamino-s-triazine

2-Chloro-4,6-diamino-s-triazine (CAAT) is a metabolite of atrazine biodegradation in soils. Atrazine chlorohydrolase (AtzA) catalyzes the dechlorination of atrazine but is unreactive with CAAT. In this study, melamine deaminase (TriA), which is 98% identical to AtzA, catalyzed deamination of CAAT to produce 2-chloro-4-amino-6-hydroxy-s-triazine (CAOT). CAOT underwent dechlorination via hydroxyatrazine ethylaminohydrolase (AtzB) to yield ammelide. This represents a newly discovered dechlorination reaction for AtzB. Ammelide was subsequently hydrolyzed by N-isopropylammelide isopropylaminohydrolase to produce cyanuric acid, a compound metabolized by a variety of soil bacteria.     

Cloning and comparison of the DNA encoding ammelide aminohydrolase and cyanuric acid amidohydrolase from three s-triazine-degrading bacterial strains.

DNA encoding the catabolism of the s-triazines ammelide and cyanuric acid was cloned from Pseudomonas sp. strain NRRLB-12228 and Klebsiella pneumoniae 99 with, as a probe, a 4.6-kb PstI fragment from a third strain, Pseudomonas sp. strain NRRLB-12227, which also encodes these activities. In strains NRRLB-12228 and 99 the ammelide aminohydrolase (trzC) and cyanuric acid amidohydrolase (trzD) genes are located on identical 4.6-kb PstI fragments which are part of a 12.4-kb DNA segment present in both strains. Strain NRRLB-12227 also carries this 12.4-kb DNA segment, except that a DNA segment of 0.8 to 1.85 kb encoding a third enzyme, ammeline aminohydrolase (trzB), has been inserted next to the ammelide aminohydrolase gene with the accompanying deletion of 1.1 to 2.15 kb of DNA. In addition, the s-triazine catabolic genes are flanked in strain NRRLB-12227 by apparently identical 2.2-kb segments that are not present in the other two strains and that seem to cause rearrangements in adjacent DNA.     

In vitro study of DNA interaction with melamine and its related compounds

In vitro studies on the interactions between native herring sperm DNA (HS-DNA) and melamine as well as its related compounds (MARCs), that is, ammeline, ammelide, and cyanuric acid, have been investigated by spectrophotometric, spectrofluorometric, melting temperature, and viscosimetric techniques. It was found that any of the MARCs might interact with HS-DNA by a groove mode of binding via hydrogen bonds. The interaction constants between any of the MARCs and HS-DNA were at 10?-10? L mol?1, determined by both spectrophotometric and spectrofluorometric methods. The thermodynamic studies suggested that the interaction processes were exothermic favored (ΔH?相似文献   

Enzymatic Degradation of Chlorodiamino-s-Triazine

2-Chloro-4,6-diamino-s-triazine (CAAT) is a metabolite of atrazine biodegradation in soils. Atrazine chlorohydrolase (AtzA) catalyzes the dechlorination of atrazine but is unreactive with CAAT. In this study, melamine deaminase (TriA), which is 98% identical to AtzA, catalyzed deamination of CAAT to produce 2-chloro-4-amino-6-hydroxy-s-triazine (CAOT). CAOT underwent dechlorination via hydroxyatrazine ethylaminohydrolase (AtzB) to yield ammelide. This represents a newly discovered dechlorination reaction for AtzB. Ammelide was subsequently hydrolyzed by N-isopropylammelide isopropylaminohydrolase to produce cyanuric acid, a compound metabolized by a variety of soil bacteria.     

Melamine deaminase and atrazine chlorohydrolase: 98 percent identical but functionally different

The gene encoding melamine deaminase (TriA) from Pseudomonas sp. strain NRRL B-12227 was identified, cloned into Escherichia coli, sequenced, and expressed for in vitro study of enzyme activity. Melamine deaminase displaced two of the three amino groups from melamine, producing ammeline and ammelide as sequential products. The first deamination reaction occurred more than 10 times faster than the second. Ammelide did not inhibit the first or second deamination reaction, suggesting that the lower rate of ammeline hydrolysis was due to differential substrate turnover rather than product inhibition. Remarkably, melamine deaminase is 98% identical to the enzyme atrazine chlorohydrolase (AtzA) from Pseudomonas sp. strain ADP. Each enzyme consists of 475 amino acids and differs by only 9 amino acids. AtzA was shown to exclusively catalyze dehalogenation of halo-substituted triazine ring compounds and had no activity with melamine and ammeline. Similarly, melamine deaminase had no detectable activity with the halo-triazine substrates. Melamine deaminase was active in deamination of a substrate that was structurally identical to atrazine, except for the substitution of an amino group for the chlorine atom. Moreover, melamine deaminase and AtzA are found in bacteria that grow on melamine and atrazine compounds, respectively. These data strongly suggest that the 9 amino acid differences between melamine deaminase and AtzA represent a short evolutionary pathway connecting enzymes catalyzing physiologically relevant deamination and dehalogenation reactions, respectively.     

Plasmid localization and organization of melamine degradation genes in Rhodococcus sp. strain Mel

Rhodococcus sp. strain Mel was isolated from soil by enrichment and grew in minimal medium with melamine as the sole N source with a doubling time of 3.5 h. Stoichiometry studies showed that all six nitrogen atoms of melamine were assimilated. The genome was sequenced by Roche 454 pyrosequencing to 13× coverage, and a 22.3-kb DNA region was found to contain a homolog to the melamine deaminase gene trzA. Mutagenesis studies showed that the cyanuric acid hydrolase and biuret hydrolase genes were clustered together on a different 17.9-kb contig. Curing and gene transfer studies indicated that 4 of 6 genes required for the complete degradation of melamine were located on an ～265-kb self-transmissible linear plasmid (pMel2), but this plasmid was not required for ammeline deamination. The Rhodococcus sp. strain Mel melamine metabolic pathway genes were located in at least three noncontiguous regions of the genome, and the plasmid-borne genes encoding enzymes for melamine metabolism were likely recently acquired.     

An examination of proton translocation and energy conservation during heterotrophic nitrification

Whether selected heterotrophic nitrifiers, as do the autotrophs, conserve energy during the oxidation of their nitrogenous substrates was studied. The examination of proton translocation of four different bacterial nitrifiers capable of pyruvic oxime [(PO), CH3-C(NOH)-COOH] nitrification and by an NH4+ oxidizing Arthrobacter sp. was initiated. Three of the PO nitrifying bacteria, all pseudomonads, oxidize hydroxylamine (NH2OH) at a greater rate than PO and yielded only stoichiometric protons when NH2OH was the reductant. The fourth bacterium, Alcaligenes faecalis ATCC 8750, an adept PO oxidizer, does not appreciably oxidize NH2OH. The bacterium displayed----H+NH2OH ratios far less than if NH2OH was stoichiometrically converted to nitrite. When given NH4+, the Arthrobacter sp. yielded proton translocation patterns which were inconsistent with the metabolic data collected concerning NH4+ oxidation. Thus no data was collected which supported energy conservation via proton translocation by these heterotrophic nitrifiers.     

Degradation of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) by Stenotrophomonas maltophilia PB1.

A mixed microbial culture capable of metabolizing the explosive RDX (hexahydro-1,3,5-trinitro-1,3,5-triazine) was obtained from soil enrichments under aerobic and nitrogen-limiting conditions. A bacterium, Stenotrophomonas maltophilia PB1, isolated from the culture used RDX as a sole source of nitrogen for growth. Three moles of nitrogen was used per mole of RDX, yielding a metabolite identified by mass spectroscopy and 1H nuclear magnetic resonance analysis as methylene-N-(hydroxymethyl)-hydroxylamine-N'-(hydroxymethyl)nitroamin e. The bacterium also used s-triazine as a sole source of nitrogen but not the structurally similar compounds octahydro-1,3,5,7-tetranitro-1,3,5,7-tetrazocine, cyanuric acid, and melamine. An inducible RDX-degrading activity was present in crude cell extracts.     

Arthrobacter aurescens TC1 metabolizes diverse s-triazine ring compounds

Arthrobacter aurescens strain TC1 was isolated without enrichment by plating atrazine-contaminated soil directly onto atrazine-clearing plates. A. aurescens TC1 grew in liquid medium with atrazine as the sole source of nitrogen, carbon, and energy, consuming up to 3,000 mg of atrazine per liter. A. aurescens TC1 is metabolically diverse and grew on a wider range of s-triazine compounds than any bacterium previously characterized. The 23 s-triazine substrates serving as the sole nitrogen source included the herbicides ametryn, atratone, cyanazine, prometryn, and simazine. Moreover, atrazine substrate analogs containing fluorine, mercaptan, and cyano groups in place of the chlorine substituent were also growth substrates. Analogs containing hydrogen, azido, and amino functionalities in place of chlorine were not growth substrates. A. aurescens TC1 also metabolized compounds containing chlorine plus N-ethyl, N-propyl, N-butyl, N-s-butyl, N-isobutyl, or N-t-butyl substituents on the s-triazine ring. Atrazine was metabolized to alkylamines and cyanuric acid, the latter accumulating stoichiometrically. Ethylamine and isopropylamine each served as the source of carbon and nitrogen for growth. PCR experiments identified genes with high sequence identity to atzB and atzC, but not to atzA, from Pseudomonas sp. strain ADP.     

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.     

Hemolysis of human erythrocytes induced by melamine-cyanurate complex

Melamine is a widely-used chemical in industries. In recent years, melamine has been found to be involved in outbreaks of renal injury in infants and animals. Pathological studies indicated that the melamine-induced acute renal failure was related to the concurrence of melamine and other triazine analogs such as cyanuric acid. In the present study, human erythrocytes were used as an in vitro model to explore the cytotoxicity of melamine and its complex with cyanuric acid. The results demonstrated that mixing melamine and cyanuric acid resulted in the formation of insoluble particles and that the insoluble melamine-cyanurate complex induced membrane damages of human erythrocytes. The membrane damages included hemolysis, K⁺ leakage, alterations in cell shape and membrane fragility, and inhibition of enzymatic activity. By contrast, either melamine or cyanuric acid alone had no effect on erythrocyte membranes. The results of this study may provide a fresh insight into the melamine toxicology.     

Inactivation of phosphorylase phosphatase by a factor from rabbit liver and its chemical characterization as glutathione disulfide.

A factor inactivating phosphorylase phosphatase was isolated from rabbit liver. The isolation procedure consisted of heat treatment at 85 degrees C, extraction with n-butyl alcohol, and chromatography on Dowex 1 and DEAE-cellulose columns. The purified factor was different from the known protein inhibitors and was shown to be tripeptide composed of equimolar amounts of glutamic acid, cysteine, and glycine. The NH2-terminal and COOH-terminal amino acids were determined as glutamic acid and glycine, respectively. The factor was finally identified as glutathione disulfide by high voltage paper electrophoresis, paper chromatography, and liquid column chromatography using an amino acid analyzer. Addition of the purified factor or glutathione disulfide converted phosphorylase phosphatase to a stable, less active enzyme species, the extent of conversion depending on the amount added. The inactivated phosphatase was completely reactivated by addition of both glutathione (or 2-mercaptoethanol) and Mn2+ and partially reactivated by adding glutathione alone. Injection of glutathione disulfide into the portal vein of rabbits caused a rapid increase in phosphorylase alpha activity in the liver. These results suggest that glutathione disulfide is involved in regulation of phosphorylase activity in vivo, by causing inactivation of phosphorylase phosphatase in the liver.     

Ring-cleaving cyanuric acid amidohydrolase activity in the atrazine-mineralizing Ralstonia basilensis M91-3

The purpose of this study was to characterize the cyanuric acid amidohydrolase reaction in Ralstonia basilensis M91-3, an atrazine-mineralizing soil bacterium. This ring fission reaction is the last aromatic step in the degradative pathway of atrazine and other s-triazines. The products and molar stoichiometry of the cyanuric acid amidohydrolase reaction were one mol biuret (H₂N·CO·NH·CO·NH₂) and one mol CO₂ per mol cyanuric acid hydrolyzed, as confirmed by ¹³C-NMR and gas chromatography. The optimum pH and temperature, substrate specificity, and kinetic parameters were also characterized for the purified enzyme. The native enzyme had two forms of different sizes, 204 kDa and 160 kDa. Each was a tetramer or pentamer of 44 kDa and 33 kDa, respectively.     

Ammonium Uptake by Rice Roots (I. Fluxes and Subcellular Distribution of 13NH4+)

The time course of 13NH4+ uptake and the distribution of 13NH4+ among plant parts and subcellular compartments was determined for 3-week-old rice (Oryza sativa L. cv M202) plants grown hydroponically in modified Johnson's nutrient solution containing 2,100, or 1000 [mu]M NH4+ (referred to hereafter as G2, G100, or G1000 plants, respectively). At steady state, the influx of 13NH4+ was determined to be 1.31, 5.78, and 10.11 [mu]mol g-1 fresh weight h-1, respectively, for G2, G100, and G1000 plants; efflux was 11, 20, and 29%, respectively, of influx. The NH4+ flux to the vacuole was calculated to be between 1 and 1.4 [mu]mol g-1 fresh weight h-1. By means of 13NH4+ efflux analysis, three kinetically distinct phases (superficial, cell wall, and cytoplasm) were identified, with t1/2 for 13NH4+ exchange of approximately 3 s and 1 and 8 min, respectively. Cytoplasmic [NH4+] was estimated to be 3.72, 20.55, and 38.08 mM for G2, G100, and G1000 plants, respectively. These concentrations were higher than vacuolar [NH4+], yet 72 to 92% of total root NH4+ was located in the vacuole. Distributions of newly absorbed 13NH4+ between plant parts and among the compartments were also examined. During a 30-min period G100 plants metabolized 19% of the influxed 13NH4+. The remainder (81%) was partitioned among the vacuole (20%), cytoplasm (41%), and efflux (20%). Of the metabolized 13N, roughly one-half was translocated to the shoots.