Peptide conjugates of benzene and toluene metabolites in English ryegrass

Biotransformation of [1-6-¹⁴C]benzene and [1-¹⁴C]toluene in English ryegrass (Lolium perenne L.) seedlings was investigated. Vapors of these compounds were absorbed by the leaves of this plant. Benzene and toluene were oxidized, forming phenol and benzoic acid, respectively. A portion of phenol and benzoic acid was bound by low-molecular-weight peptides forming conjugates. A qualitative amino acid composition of the peptides involved in the conjugation was determined. After removing plants from the atmosphere containing [1-6-¹⁴C]benzene and [1-¹⁴C]toluene, the radioactivity of the conjugates gradually decreased. This process was accompanied by the evolution of ¹⁴CO₂, indicating the breakdown of these conjugates. Radioactive compounds thus formed were oxidized, yielding carbon dioxide. A portion of phenol and benzoic acid, along with peptide conjugation, was subjected to further oxidative transformations up to disruption of the aromatic ring. By this pathway, nonvolatile carboxylic acids, such as muconic, fumaric, succinic, malic, malonic, glycolic, and glyoxylic, were formed. Using electron microscopy, a damaging effect of benzene on the cell ultrastructure of English ryegrass leaves was shown, and this toxic effect depended on the benzene concentration.     

Niacin Biosynthesis in Seedlings of Zea mays

Evidence obtained from incubation of corn (Zea mays cv. Golden Bantam) seedlings in dl-[benzene ring-U-(14)C]tryptophan, l-[5-(3)H]tryptophan, l-[U-(14)C]aspartate and [U-(14)C]glycerol indicates that niacin is synthesized in these plants via oxidative degradation of tryptophan. Aspartate and glycerol do not appear to be precursors of niacin in corn seedlings.     

Ligninase of Phanerochaete chrysosporium. Mechanism of its degradation of the non-phenolic arylglycerol beta-aryl ether substructure of lignin.

This study examined the ligninase-catalysed degradation of lignin model compounds representing the arylglycerol beta-aryl ether substructure, which is the dominant one in the lignin polymer. Three dimeric model compounds were used, all methoxylated in the 3- and 4-positions of the arylglycerol ring (ring A) and having various substituents in the beta-ether-linked aromatic ring (ring B), so that competing reactions involving both rings could be compared. Studies of the products formed and the time courses of their formation showed that these model compounds are oxidized by ligninase (+ H2O2 + O2) in both ring A and ring B. The major consequence with all three model compounds is oxidation of ring A, leading primarily to cleavage between C(alpha) and C(beta) (C(alpha) being proximal to ring A), and to a lesser extent to the oxidation of the C(alpha)-hydroxy group to a carbonyl group. Such C(alpha)-oxidation deactivates ring A, leaving only ring B for attack. Studies with C(alpha)-carbonyl model compounds corresponding to the three basic model compounds revealed that oxidation of ring B leads in part to dealkoxylations (i.e. to cleavage of the glycerol beta-aryl ether bond and to demethoxylations), but that these are minor reactions in the model compounds most closely related to lignin. Evidence is also given that another consequence of oxidation of ring B in the C(alpha)-carbonyl model compounds is formation of unstable cyclohexadienone ketals, which can decompose with elimination of the beta-ether-linked aromatic ring. The mechanisms proposed for the observed reactions involve initial formation of aryl cation radicals in either ring A or ring B. The cation radical intermediate from one of the C(alpha)-carbonyl model compounds was identified by e.s.r. spectroscopy. The mechanisms are based on earlier studies showing that ligninase acts by oxidizing appropriately substituted aromatic nuclei to aryl cation radicals [Kersten, Tien, Kalyanaraman & Kirk (1985) J. Biol. Chem. 260, 2609-2612; Hammel, Tien, Kalyanaraman & Kirk (1985) J. Biol. Chem. 260, 8348-8353].     

Fragments formed by the side chain cleavage of a 20-aryl analog of 20alpha-hydroxycholesterol by adrenal mitochondria.

An analog of 20alpha-hydroxycholesterol, (20R)-20-phenyl-5-pregnene-3beta,20-diol, which is completely substituted at C-22 was prepared with radioisotopes at various positions. The analog labeled with 3H at C-M and 14C at C-4 and C-IU was converted into radioactive pregnenolone by an enzyme preparation derived from adrenal mitochondria. Cleavage of the phenyl analog labeled with 3H in the aromatic ring by the same enzyme preparation led to the formation of [3H]phenol. Using the substrate doubly labeled with 14C at C-4 and 3H in the aromatic ring, it appeared that the products of the reactions, pregnenolone and phenol, were formed in equal amounts. During incubation of the side chain labeled substrate, another labeled fragment was formed. It was identified as acetophenone, a product resulting from cleavage of the C17,20 bond. The steroidal fragment corresponding to this C8 ketone was traced using nuclear label analog. From its nonpolar chromatographic properties it appears to be a C-17-deoxy-C19 steroid.     

A new class of synthetic auxin transport inhibitors

Auxin transport inhibition by a new class of synthetic plant growth regulants, the 2-(3-aryl-5-pyrazolyl)benzoic acids, was examined in bean (Phaseolus vulgaris L.) using the donor-receiver agar cylinder technique. These compounds can be prepared by the dehydrogenation and ring cleavage of compounds like DPX-1840 (2-(4-methoxyphenyl)-3,3adihydro-8H-pyrazolo[5,1-a] isoindol-8-one) which was previously reported (Plant Physiol. 1972. 50: 322-327) to be a potent inhibitor of auxin transport. These new growth regulators inhibit auxin transport more than DPX-1840 does as evidenced by their consistently greater reduction of basipetal auxin transport capacity in bean when incorporated into the receiver agar cylinder or applied foliarly to intact plants. Direct comparisons of the effect of DPX-1840, its dehydrogenation product (2-(4-methoxyphenyl)-8H-pyrazolo [5,1-a]isoindol-8-one), and its open-ring form (2-(3-(4-methoxyphenyl)-5-pyrazolyl) benzoic acid) on auxin transport indicated the following order of activity: ring-open > dehydrogenated form > DPX-1840. DPX-1840-(14)C, applied at 0.5 mg/l to etiolated bean hypocotyl hooks followed by extraction and thin layer chromatography, indicated the biological conversion of DPX-1840 to its open-ring form. Collectively, these results suggest that the biologically active forms of DPX-1840-type compounds are the open-ring (2-(3-aryl-5-pyrazolyl) benzoic acids.     

Detoxification of Formaldehyde by the Spider Plant (Chlorophytum comosum L.) and by Soybean (Glycine max L.) Cell-Suspension Cultures

The phytotoxicity of formaldehyde for spider plants (Chlorophytum comosum L.), tobacco plants (Nicotiana tabacum L. cv Bel B and Bel W3), and soybean (Glycine max L.) cell-suspension cultures was found to be low enough to allow metabolic studies. Spider plant shoots were exposed to 7.1 [mu]L L-1 (8.5 mg m-3) gaseous [14C]-formaldehyde over 24 h. Approximately 88% of the recovered radioactivity was plant associated and was found to be incorporated into organic acids, amino acids, free sugars, and lipids as well as cell-wall components. Similar results were obtained upon feeding [14C]formaldehyde from aqueous solution to aseptic soybean cell-suspension cultures. Serine and phosphatidylcholine were identified as major metabolic products. Spider plant enzyme extracts contained two NAS+-dependent formaldehyde dehydrogenase activities with molecular mass values of about 129 and 79 kD. Only the latter enzyme activity required glutathione as an obligatory second cofactor. It had an apparent Km value of 30 [mu]M for formaldehyde and an isoelectric point at pH 5.4. Total cell-free dehydrogenase activity corresponded to 13 [mu]g formaldehyde oxidized h-1 g-1 leaf fresh weight. Glutathione-dependent formaldehyde dehydrogenases were also isolated from shoots and leaves of Equisetum telmateia and from cell-suspension cultures of wheat (Triticum aestivum L.) and maize (Zea mays L.). The results obtained are consistent with the concept of indoor air decontamination with common room plants such as the spider plant. Formaldehyde appears to be efficiently detoxified by oxidation and subsequent C1 metabolism.     

Biosynthetis of phytoquinones. Biosynthetic origins of the nuclei and satellite methyl groups of plastoquinone, tocopherols and tocopherolquinones in maize shoots, bean shoots and ivy leaves

1. By using dl-[ring-(14)C]phenylalanine, dl-[beta-(14)C]phenylalanine, dl-[alpha-(14)C]-tyrosine and dl-[beta-(14)C]tyrosine it was shown that in maize shoots (Zea mays) the nucleus and one nuclear methyl group of each of the following compounds, plastoquinone, gamma-tocopherol (aromatic nucleus) and alpha-tocopherolquinone, are formed from the nuclear carbon atoms and beta-carbon atom respectively of either exogenous phenylalanine or exogenous tyrosine. With ubiquinone only the aromatic ring of the amino acid is used in the synthesis of the quinone nucleus. Chemical degradation of plastoquinone and gamma-tocopherol molecules labelled from l-[U-(14)C]tyrosine established that a C(6)-C(1) unit directly derived from the amino acid is involved in the synthesis of these compounds. Radioactivity from [beta-(14)C]cinnamic acid is not incorporated into plastoquinone, tocopherols or tocopherolquinones, demonstrating that the C(6)-C(1) unit is not formed from any of the C(6)-C(1) phenolic acids associated with the metabolism of this compound. 2. The incorporation of radioactivity from l-[U-(14)C]tyrosine, dl-[beta-(14)C]tyrosine and dl-[U-(14)C]phenylalanine into bean shoots (Phaseolus vulgaris) and dl-[beta-(14)C]tyrosine and l-[Me-(14)C]methionine into ivy leaves (Hedera helix) was also investigated. Similar results were obtained to those reported for maize, except that in beans phenylalanine is only used for ubiquinone biosynthesis. This is attributed to the absence of phenylalanine hydroxylase from these tissues. In ivy leaves it is found that the beta-carbon atom of tyrosine gives rise to the 8-methyl group of delta-tocopherol, and it is suggested that for all other compounds examined it will give rise to the nuclear methyl group meta to the polyprenyl unit. 3. Preliminary investigations with the alga Euglena gracilis showed that in this organism ring-opening of tyrosine occurs to such an extent that the incorporation data from radiochemical experiments are meaningless. 4. The above results, coupled with previous observations, are interpreted as showing that in higher plants the nucleus of ubiquinone can be formed from either phenylalanine or tyrosine by a pathway involving as intermediates p-coumaric acid and p-hydroxybenzoic acid. Plastoquinone, tocopherols and alpha-tocopherolquinone are formed from p-hydroxyphenylpyruvate by a pathway in which the aromatic ring and C-3 of the side chain give rise respectively to the nucleus and to one nuclear methyl group. 5. Dilution experiments provided evidence that in maize shoots p-hydroxyphenylpyruvic acid and homogentisic acid (produced from p-hydroxyphenylpyruvic acid) are involved in plastoquinone biosynthesis, and presumably the biosynthesis of related compounds: however, other possible intermediates in the conversion including toluquinol (the aglycone of the proposed key intermediate) showed no dilution effects. Further, radioactivity from [Me-(14)C]toluquinol is not incorporated into any of the compounds examined. 6. Dilution experiments with 3,4-dihydroxybenzaldehyde and radioactive-labelling experiments with 3,4-dihydroxy[U-(14)C]benzoic acid demonstrated that these compounds are not involved in the biosynthesis of either ubiquinone or phylloquinone in maize shoots. 7. Evidence is also presented to show that in maize shoots ring-opening of the aromatic amino acids takes place. The suggestion is offered that this may take place via homogentisic acid, as in animals and some micro-organisms.     

Phenol conjugation with peptides and final transformations of conjugates in English ryegrass seedlings

[ 1-14C] Phenol transformation in English ryegrass (Lolium perenne L.) sterile seedlings was studied. The compound studied was assimilated by a plant through leaves as vapor. Phenol was bound with ryegrass low-molecular-weight peptides producing phenol-peptide conjugates. Conjugation with endogenous peptides is one of the main pathways of phenol detoxication in ryegrass. Nearly three fifths of phenol assimilated is conjugated with low-molecular-weight peptides. After removal of the plant from the labeled phenol-containing atmosphere, the content of conjugation products gradually decreased, followed by excretion of labeled carbon dioxide. This fact indicates that the conjugates are destructed and the carbon atoms of their radioactive component are oxidized to carbon dioxide. Almost one third of assimilated phenol is transformed via the oxidation pathway, but a small part of it is irreversibly bound with biopolymer molecules.     

The metabolism of fluoroacetate in lettuce

1. Whole lettuce plants were incubated with (1) [1-(14)C]acetate, (2) fluoroacetate followed by [1-(14)C]acetate, (3) fluoro[1-(14)C]acetate, (4) fluoro[2-(14)C]acetate or (5) S-carboxy[(14)C]methylglutathione. 2. Fluoroacetate did not affect the expiration of (14)CO(2) from [1-(14)C]acetate and only a small amount of (14)CO(2) was produced from either fluoro[1-(14)C]-acetate or fluoro[2-(14)C]acetate in 43h. 3. Fluoroacetate at 50mg/kg wet wt. doubled the plant citrate concentration after 43h incubation, and depending on the age and size of the plant 50-100% of the compound was metabolized. 4. With both fluoro[1-(14)C]acetate and fluoro[2-(14)C]acetate all the radioactivity except that in the CO(2) was found in the water-soluble acid fraction. About 2% was in fluorocitrate and the remainder, apart from unchanged fluoroacetate, was in a number of compounds devoid of fluorine but containing nitrogen and sulphur. These were peptide-like and could be separated by chromatography on an amino acid analyser. 5. Identical compounds were obtained from the spontaneous reaction between iodo[2-(14)C]acetate and glutathione, the major product being S-carboxymethylglutathione. 6. S-Carboxymethylcysteine was also isolated and its mass spectrum compared with a commercial sample. 7. Reaction rates of all the monohaloacetates with glutathione were studied at pH7 at 25 degrees C. No reaction was observed with fluoroacetate. 8. The metabolism of fluoroacetate by lettuce is discussed in relation to that of aliphatic and aromatic halogen compounds, including fluoroacetate, by mammalian liver and to the metabolism of fluoroacetate by different plants reported by other workers.     

Evidence implicating dimethylsulfoniopropionaldehyde as an intermediate in dimethylsulfoniopropionate biosynthesis.

3-Dimethylsulfoniopropionate (DMSP) is an osmoprotectant accumulated by certain flowering plants and algae. In Wollastonia biflora (L.) DC. (Compositae) the first intermediate in DMSP biosynthesis has been shown to be S-methylmethionine (SMM) (A.D. Hanson, J. Rivoal, L. Paquet, D.A. Gage [1994] Plant Physiol 105: 103-110). Other possible intermediates were investigated by radiolabeling methods using W. biflora leaf discs. In pulse-chase experiments with [35S]SMM, 3-dimethylsulfoniopropionaldehyde (DMSP-ald) acquired label rapidly and lost it during the chase period. Conversely, 3-dimethylsulfoniopropylamine (DMSP-amine), 3-dimethylsulfoniopropionamide (DMSP-amide), and 4-dimethylsulfonio-2-hydroxybutyrate (DMSHB) labeled slowly and continuously during both pulse and chase. When unlabeled compounds were supplied along with [35S]SMM, DMSP-ald promoted [35S]DMSP-ald accumulation but DMSHB, DMSP-amide, and DMSP-amine had no such trapping effect. These data indicate that DMSP-ald is an intermediate in DMSP biosynthesis and that the other three compounds are not. Consistent with this, [35S]DMSHB was not metabolized to DMSP. Although [14C]DMSP-amine and [14C]DMSP-amide were converted slowly to DMSP, similar or higher conversion rates were found in plants that do not naturally accumulate DMSP, indicating that nonspecific reactions were responsible. These nonaccumulating species did not form [35S]DMSP-ald from [35S]SMM, implying that DMSP-ald is specific to DMSP biosynthesis. W. biflora leaf discs catabolized supplied sulfonium compounds to dimethylsulfide at differing rates, in the order DMSP-ald >> DMSP-amine > SMM > DMSP-amide > DMSHB > DMSP.     

Herbicidal Activity of an Isopropylmalate Dehydrogenase Inhibitor

Isopropylmalate dehydrogenase (IPMDH) is the third enzyme specific to leucine biosynthesis. It catalyzes the oxidative decarboxylation of 3-isopropylmalate (3-IPM) to 2-ketoisocaproic acid. The partially purified enzyme from pea (Pisum sativum L.) shows a broad pH optimum of 7.8 to 9.1 and has Km values for 3-IPM and NAD of 18 and 40 [mu]M, respectively. O-Isobutenyl oxalylhydroxamate (O-IbOHA) has been discovered to be an excellent inhibitor of the pea IPMDH, with an apparent inhibitor constant of 5 nM. As an herbicide, O-IbOHA showed only moderate activity on a variety of broadleaf and grass species. We characterized the herbicidal activity of O-IbOHA on corn (Zea mays L.), a sensitive species; giant foxtail (Setaria faberi) and morning glory (Ipomoea purpurea [L.] Roth), moderately tolerant species; and soybean [Glycine max L. Merr.), a tolerant species. Differences in tolerance among the species were not due to differences in the sensitivity of IPMDH. Studies with [14C]O-IbOHA suggested that uptake and translocation were not major limitations for herbicidal activity, nor were they determinants of tolerance. Moreover, metabolism could not account for the difference in tolerance of corn, foxtail, and morning glory, although it might account for the tolerance of soybean. Herbicidal activity on all four species was correlated with the accumulation of 3-IPM in the plants.     

Biotransformation of benzothiophene by isopropylbenzene-degrading bacteria.

Isopropylbenzene-degrading bacteria, including Pseudomonas putida RE204, transform benzothiophene to a mixture of compounds. Induced strain RE204 and a number of its Tn5 mutant derivatives were used to accumulate these compounds and their precursors from benzothiophene. These metabolites were subsequently identified by 1H and 13C nuclear magnetic resonance spectroscopy and gas chromatography-mass spectrometry. When strain RE204 was incubated with benzothiophene, it produced a bright yellow compound, identified as trans-4-[3-hydroxy-2-thienyl]-2-oxobut-3-enoate, formed by the rearrangement of cis-4-(3-keto-2,3-dihydrothienyl)-2-hydroxybuta-2,4-dieno ate, the product of 3-isopropylcatechol-2,3-dioxygenase-catalyzed ring cleavage of 4,5-dihydroxybenzothiophene, as well as 2-mercaptophenylglyoxalate and 2'-mercaptomandelaldehyde. A dihydrodiol dehydrogenase-deficient mutant, strain RE213, converted benzothiophene to cis-4,5-dihydroxy-4,5-dihydrobenzothiophene and 2'-mercaptomandelaldehyde; neither trans-4-[3-hydroxy-2-thienyl]-2-oxobut-3-enoate nor 2-mercaptophenylglyoxalate was detected. Cell extracts of strain RE204 catalyzed the conversion of cis-4,5-dihydroxy-4,5-dihydrobenzothiophene to trans-4-[3-hydroxy-2-thienyl]-2-oxobut-3-enoate in the presence of NAD+. Under the same conditions, extracts of the 3-isopropylcatechol-2,3-dioxygenase-deficient mutant RE215 acted on cis-4,5-dihydroxy-4,5-dihydrobenzothiophene, forming 4,5-dihydroxybenzothiophene. These data indicate that oxidation of benzothiophene by strain RE204 is initiated at either ring. Transformation initiated at the 4,5 position on the benzene ring proceeds by three enzyme-catalyzed reactions through ring cleavage. The sequence of events that occurs following attack at the 2,3 position of the thiophene ring is less clear, but it is proposed that 2,3 dioxygenation yields a product that is both a cis-dihydrodiol and a thiohemiacetal, which as a result of this structure undergoes two competing reactions: either spontaneous opening of the ring, yielding 2'-mercaptomandelaldehyde, or oxidation by the dihydrodiol dehydrogenase to another thiohemiacetal, 2-hydroxy-3-oxo-2,3-dihydrobenzothiophene, which is not a substrate for the ring cleavage dioxygenase but which spontaneously opens to form 2-mercaptophenylglyoxaldehyde and subsequently 2-mercaptophenylglyoxalate. The yellow product, trans-4-[3-hydroxy-2-thienyl]-2-oxobut-3-enoate, is a structural analog of trans-o-hydroxybenzylidenepyruvate, an intermediate of the naphthalene catabolic pathway; extracts of recombinant bacteria containing trans-o-hydroxybenzylidenepyruvate hydratase-aldolase catalyzed the conversion of trans-4-[3-hydroxy-2-thienyl]-2-oxobut-3-enoate to 3-hydroxythiophene-2-carboxaldehyde, which could then be further acted on, in the presence of NAD+, by extracts of recombinant bacteria containing the subsequent enzyme of the naphthalene pathway, salicylaldehyde dehydrogenase.     

Divergent synthesis of kinase inhibitor derivatives,leading to discovery of selective Gck inhibitors

We accomplished divergent synthesis of potent kinase inhibitor BAY 61-3606 (1) and 27 derivatives via conjugation of imidazo[1,2-c]pyrimidine and indole ring compounds with aromatic (including pyridine) derivatives by means of palladium-catalyzed cross-coupling reaction. Spleen tyrosine kinase (Syk) and germinal center kinase (Gck, MAP4K2) inhibition assays showed that some of the synthesized compounds were selective Gck inhibitors.     

Conjugation reactions involving maleimides and phosphorothioate oligonucleotides

Phosphorothioate diester oligonucleotides proved to be fully compatible with maleimides in the context of two different conjugation reactions: (a) reaction of (5')diene-[phosphorothioate oligonucleotides] with maleimido-containing compounds to afford the Diels-Alder cycloadduct; (b) conjugation of (5')maleimido-[phosphorothioate oligonucleotides] with thiol-containing compounds. No evidence of reaction between phosphorothioate diesters and maleimides was found in any of these processes. Importantly, in the preparation of (5')maleimido-[phosphorothioate oligonucleotides] from [protected maleimido]-[phosphorothioate oligonucleotides], which requires the maleimide to be deprotected by retro-Diels-Alder reaction (heating for 3-4 h in toluene at 90 °C), no addition of phosphorothioate diester to the maleimide was found either. Finally, maleimide-[phosphorothioate monoester] conjugation was also explored for comparison purposes.     

Monitoring flux through the oxidative pentose phosphate pathway using [1-14C]gluconate

The aim of this work was to examine the metabolism of exogenous gluconate by a 4-day-old cell suspension culture of Arabidopsis thaliana (L.) Heynh. Release of (14)CO(2) from [1-(14)C]gluconate was dependent on the concentration in the medium and could be resolved into a substrate-saturable component (apparent K(m) of approximately 0.4 mM) and an unsaturable component. At an external concentration of 0.3 mM, the rate of decarboxylation of applied gluconate was 0.2% of the rate of oxygen consumption by the cells. There was no effect of 0.3 mM gluconate on the rate of oxygen consumption, or on the rate of (14)CO(2) release from either [1-(14)C]glucose or [6-(14)C]glucose by the culture. The following observations argue that gluconate taken up by the cells is metabolised by direct phosphorylation to 6-phosphogluconate and subsequent decarboxylation through 6-phosphogluconate dehydrogenase. First, more than 95% of the label released from [1-(14)C]gluconate during metabolism by the cell culture was recovered as (14)CO(2). Secondly, inhibition of the oxidative pentose phosphate pathway (OPPP) by treatment with 6-aminonicotinamide preferentially inhibited release of (14)CO(2) from [1-(14)C]gluconate relative to that from [1-(14)C]glucose. Thirdly, perturbation of glucose metabolism by glucosamine did not affect (14)CO(2) from [1-(14)C]gluconate. Fourth, stimulation of the OPPP by phenazine methosulphate stimulated release of (14)CO(2) from [1-(14)C]gluconate to a far greater extent than that from [1-(14)C]glucose. It is proposed that measurement of (14)CO(2) from [1-(14)C]gluconate provides a simple and sensitive technique for monitoring flux through the OPPP pathway in plants.     

Fatty acid synthesis by slices from developing leaves

Fatty acid synthesis was studied in successive leaf sections from the base to the tip of developing barley (Hordeum vulgare L.), maize (Zea mays L.), rye grass (Lolium perenne L.) and wheat (Triticum aestivium L.) leaves. The basal regions of the leaves had the lowest rates of fatty acid synthesis and accumulated small amounts of very long chain fatty acids. Fatty acid synthesis was highest in the middle leaf sections in all four plants. Linolenic acid synthesis from [1-¹⁴C]acetate was highest in the distal leaf sections of rye grass. The labelling of the fatty acids of individual lipids of rye grass was examined and it was found that [¹⁴C]linolenic acid was highest in the galactolipids. Synthesis of this acid in the galactolipids was most active in leaf segment C. Only traces of [¹⁴C]linolenic acid were ever found in phosphatidylcholine and it is concluded that this phospholipid cannot serve as a substrate for linoleic acid desaturation in rye grass. The synthesis of fatty acids was sensitive to arsenite, fluoride and the herbicide EPTC. The latter was only inhibitory towards those leaf segments which made very long chain fatty acids. Formation of fatty acids from [1-¹⁴C]acetate was also studied in chloroplasts prepared from successive leaf sections of rye grass. Chloroplasts isolated from the middle leaf sections had the highest activity. Palmitic and oleic acids were the main fatty acid products in all chloroplast preparations. Linolenic acid synthesis was highest in chlorplasts isolated from the distal leaf sections of rye grass.     

Roles of Oxygen and the Intestinal Microflora in the Metabolism of Lignin-Derived Phenylpropanoids and Other Monoaromatic Compounds by Termites

Prompted by our limited understanding of the degradation of lignin and lignin-derived aromatic metabolites in termites, we studied the metabolism of monoaromatic model compounds by termites and their gut microflora. Feeding trials performed with [ring-U-(sup14)C]benzoic acid and [ring-U-(sup14)C]cinnamic acid revealed the general ability of termites of the major feeding guilds (wood and soil feeders and fungus cultivators) to mineralize the aromatic nucleus. Up to 70% of the radioactive label was released as (sup14)CO(inf2); the remainder was more or less equally distributed among termite bodies, gut contents, and feces. Gut homogenates of the wood-feeding termites Nasutitermes lujae (Wasmann) and Reticulitermes flavipes (Kollar) mineralized ring-labeled benzoic or cinnamic acid only if oxygen was present. In the absence of oxygen, benzoate was not attacked, and cinnamate was only reduced to phenylpropionate. Similar results were obtained with other, nonlabeled lignin-related phenylpropanoids (ferulic, 3,4-dihydroxycinnamic, and 4-hydroxycinnamic acids), whose ring moieties underwent degradation only if oxygen was present. Under anoxic conditions, the substrates were merely modified (by side chain reduction and demethylation), and this modification occurred at the same time as a net accumulation of phenylpropanoids formed endogenously in the gut homogenate, a phenomenon not observed under oxic conditions. Enumeration by the most-probable-number technique revealed that each N. lujae gut contained about 10(sup5) bacteria that were capable of completely mineralizing aromatic substrates in the presence of oxygen (about 10(sup8) bacteria per ml). In the absence of oxygen, small numbers of ring-modifying microorganisms were found (<50 bacteria per gut), but none of these microorganisms were capable of ring cleavage. Similar results were obtained with gut homogenates of R. flavipes, except that a larger number of anaerobic ring-modifying microorganisms was present (>5 x 10(sup3) bacteria per gut). Neither inclusion of potential cosubstrates (H(inf2), pyruvate, lactate) nor inclusion of hydrogenotrophic partner organisms resulted in anoxic ring cleavage in most-probable-number tubes prepared with gut homogenates of either termite. The oxygen dependence of aromatic ring cleavage by the termite gut microbiota is consistent with the presence, and uptake by microbes, of O(inf2) in the peripheral region of otherwise anoxic gut lumina (as reported in the accompanying paper [A. Brune, D. Emerson, and J. A. Breznak, Appl. Environ. Microbiol. 61:2681-2687, 1995]). Taken together, our results indicate that microbial degradation of plant aromatic compounds can occur in termite guts and may contribute to the carbon and energy requirement of the host.     

Effects of co-occurring aromatic hydrocarbons on degradation of individual polycyclic aromatic hydrocarbons in marine sediment slurries.

Rates of polycyclic aromatic hydrocarbon (PAH) degradation and mineralization were influenced by preexposure to alternate PAHs and a monoaromatic hydrocarbon at relatively high (100 ppm) concentrations in organic-rich aerobic marine sediments. Prior exposure to three PAHs and benzene resulted in enhanced [14C]naphthalene mineralization, while [14C]anthracene mineralization was stimulated only by benzene and anthracene preexposure. Preexposure of sediment slurries to phenanthrene stimulated the initial degradation of anthracene. Prior exposure to naphthalene stimulated the initial degradation of phenanthrene but had no effect on either the initial degradation or mineralization of anthracene. For those compounds which stimulated [14C]anthracene or [14C]naphthalene mineralization, longer preexposures (2 weeks) to alternative aromatic hydrocarbons resulted in an even greater stimulation response. Enrichment with individual PAHs followed by subsequent incubation with one or two PAHs showed no alteration in degradation patterns due to the simultaneous presence of PAHs. The evidence suggests that exposure of marine sediments to a particular PAH or benzene results in the enhanced ability of these sediments to subsequently degrade that PAH as well as certain other PAHs. The enhanced degradation of a particular PAH after sediments have been exposed to it may result from the selection and proliferation of specific microbial populations capable of degrading it. The enhanced degradation of other PAHs after exposure to a single PAH suggests that the populations selected have either broad specificity for PAHs, common pathways of PAH degradation, or both.     

Auxin promotes gibberellin biosynthesis in decapitated tobacco plants

Excision of the apical bud (decapitation) of tobacco (Nicotiana tabacum L.) plants reduced the endogenous levels of indole-3-acetic acid (IAA), gibberellin A20 (GA20), and GA1 (the bioactive GA), in internode tissue below the excision site. Application of IAA to the stump of decapitated plants dramatically increased GA20 content, to a level 3-fold greater than in intact plants. Gibberellin A1 content was also increased by IAA. Decapitation reduced the conversion of [14C]GA19 to [14C]GA20 and of [14C]GA20 to [14C]GA1, and appeared to promote the deactivation pathway [14C]GA20 to [14C]GA29 to [14C]GA29-catabolite. Application of auxin counteracted these effects, but did not restore the conversion of [14C]GA20 to [14C]GA1 to the level found in intact plants. The results indicate that auxin is necessary for normal GA biosynthesis in stems of tobacco.     

Effects of co-occurring aromatic hydrocarbons on degradation of individual polycyclic aromatic hydrocarbons in marine sediment slurries

Rates of polycyclic aromatic hydrocarbon (PAH) degradation and mineralization were influenced by preexposure to alternate PAHs and a monoaromatic hydrocarbon at relatively high (100 ppm) concentrations in organic-rich aerobic marine sediments. Prior exposure to three PAHs and benzene resulted in enhanced [14C]naphthalene mineralization, while [14C]anthracene mineralization was stimulated only by benzene and anthracene preexposure. Preexposure of sediment slurries to phenanthrene stimulated the initial degradation of anthracene. Prior exposure to naphthalene stimulated the initial degradation of phenanthrene but had no effect on either the initial degradation or mineralization of anthracene. For those compounds which stimulated [14C]anthracene or [14C]naphthalene mineralization, longer preexposures (2 weeks) to alternative aromatic hydrocarbons resulted in an even greater stimulation response. Enrichment with individual PAHs followed by subsequent incubation with one or two PAHs showed no alteration in degradation patterns due to the simultaneous presence of PAHs. The evidence suggests that exposure of marine sediments to a particular PAH or benzene results in the enhanced ability of these sediments to subsequently degrade that PAH as well as certain other PAHs. The enhanced degradation of a particular PAH after sediments have been exposed to it may result from the selection and proliferation of specific microbial populations capable of degrading it. The enhanced degradation of other PAHs after exposure to a single PAH suggests that the populations selected have either broad specificity for PAHs, common pathways of PAH degradation, or both.