The effect of nitrate and nitrite on oxygen evolution and carbon-dioxide assimilation and the reduction of nitrate and nitrite by intact chloroplasts

Summary Intact chloroplasts isolated from spinach reduced NO₃ ^- and NO₂ ^- in the light without the addition of either co-factors or added enzymes. The maximum rate observed, however, for the reduction of NO₃ ^- was approximately 3Moles hr^-1 mg^-1 (chlorophyll) and for NO₂ ^- 6 Moles hr^-1 mg^-1 (chlorophyll). These rates were consistent with the enzyme content of whole chloroplasts, but much lower than those found in whole leaf extracts.The addition of both NO₃ ^- and NO₂ ^- in low concentrations resulted in transient increases in both O₂ evolution and CO₂ fixation. The increases in oxygen evolution were not consistent in amount and bore no relation to the amount of substrate reduced. Similar transients were observed in a number of experiments when NaCl or NH₄Cl were added.The addition of NO₂ ^- at concentrations of 10^-4 M and above resulted in marked inhibition of both O₂ evolution and CO₂ fixation. NO₂ ^- appears to inhibit by blocking the reduction of NADP. NO₃ ^- at similar concentrations had no such effect.An increase in the soluble amino nitrogen content of the chloroplasts was observed when NO₃ ^- or NO₂ ^- was reduced. There was, however, no increase in the incorporation of ¹⁴C from ¹⁴CO₂ into amino acids under these conditions. Even with the addition of ammonia the amount of ¹⁴C incorporated into the amino acids was not changed from less than 5% of the total ¹⁴C fixed. We conclude that while intact chloroplasts do have the ability to reduce both NO₃ ^- and NO₂ ^- at low rates, they do not synthesize appreciable amounts of amino acid directly, and this fact must be considered when formulating any pathways for nitrogen metabolism during photosynthesis.Supported in part by the National Research Council of Canada.     

Effects of oxygen on Pseudomonas nautica growth on n-alkane with or without nitrate

The denitrifying marine bacterium, Pseudomonas nautica 617, can grow on lactate aerobically or anaerobically in presence of nitrate with generation times of 1.5 and 3 h respectively. The growth on heptadecane occurs only in presence of oxygen whatever its concentration with a genrration time of 8.5 h. The influence of oxygen, carbon sources (lactate or heptadecane) and nitrate was examined on O₂, NO₃ ^-, NO₂ ^- consumption, on nitrate and nitrite reductases activities, on cell yields, and on the ratio of CO₂ produced per unit of biomass. Pseudomonas nautica metabolizes hydrocarbons under denitrifying conditions in the presence of oxygen. Nitrate and nitrite are used during growth on lactate and heptadecane up to oxygen concentrations corresponding to 50 and 30% of air-saturation, respectively. When growth on n-alkane was not oxygen-limited (above 50% of air-saturation) the catabolism decreases in favour of carbon incorporation into the cell. Nitrate and nitrite reductases were strongly inhibited after 20% of airsaturation in the presence of lactate as growth substrate. With n-alkane, only the nitrate reductase activity was greatly reduced.     

Effects of<Emphasis Type="Italic"> Vitreoscilla</Emphasis> hemoglobin on the 2,4-dinitrotoluene (2,4-DNT) dioxygenase activity of<Emphasis Type="Italic"> Burkholderia</Emphasis> and on 2,4-DNT degradation in two-phase bioreactors

Expression of vgb, encoding Vitreoscilla hemoglobin (VHb), in Burkholderia strain YV1 was previously shown to improve cell growth and enhance 2,4-dinitrotoluene (2,4-DNT) degradation compared with control strain DNT, especially under hypoxic conditions. In the work reported here, the ratio of 2,4-DNT degraded to oxygen uptake was approximately 5-fold larger for strain YV1 than for strain DNT. The addition of purified VHb to cytosolic fractions of strain DNT increased 2,4-DNT degradation 1.5-fold, compared with 1.1-fold for control bovine Hb, but increased the 2,4-DNT degradation 2.7-fold when added to partially purified 2,4-DNT dioxygenase, compared with 1.3-fold for bovine Hb. This suggests a direct transfer of oxygen from VHb to the oxygenase. In a bioreactor at high 2,4-DNT concentration (using 100 ml oleyl alcohol containing 2 g 2,4-DNT as the second phase) with 1.5 l culture, both strains could remove 0.8 g 2,4-DNT by 120 h; and, under the same conditions in a fed-batch reactor, the degradation increased to 1 g for strain YV1 but not for strain DNT.     

Transgenic tobacco plants overexpressing a cold-adaptive nitroreductase gene exhibited enhanced 2,4-dinitrotoluene detoxification rate at low temperature

Abstract

Plants encounter many environmental factors such as low and high temperatures during phytoremediation processes. In this study, our aim was to produce the transgenic tobacco plants by using a newly characterized bacterial nitroreductase, Ntr, which was active at a broad range temperature in order to detoxify 2,4-dinitrotoluene (2,4-DNT) at lower temperature. The presence of Ntr and its heterologous expression was verified in T1 transgenic plants and their growing ability were determined under toxic amount of 2,4-DNT (35?µM). Fresh weight and dry weight of transgenic plants were significantly higher than wild type (WT) under toxic 2,4-DNT at 22?°C, indicating higher growth capacity of the transgenics. Transgenic plants also showed a higher tolerance than WT when exposed to 2,4-DNT at 15?°C. Moreover, transformation rate of 2,4-DNT was gradually decreased through decreasing temperatures in WT media, however, it was increased through decreasing temperatures in transgenic plant TR3-25 media and it had the highest transformation rate (54%) of 2,4-DNT at 4?°C. Correlatively, 2,4-DNT treatment at 4?°C led to a significant decrease in H₂O₂ level in transgenic plants. Thus, transgenic plants overexpressing nitroreductase might have an important advantage for phytoremediation of toxic nitroaromatic compounds in field applications at low temperatures.     

Aerobic Degradation of Dinitrotoluenes and Pathway for Bacterial Degradation of 2,6-Dinitrotoluene

An oxidative pathway for the mineralization of 2,4-dinitrotoluene (2,4-DNT) by Burkholderia sp. strain DNT has been reported previously. We report here the isolation of additional strains with the ability to mineralize 2,4-DNT by the same pathway and the isolation and characterization of bacterial strains that mineralize 2,6-dinitrotoluene (2,6-DNT) by a different pathway. Burkholderia cepacia strain JS850 and Hydrogenophaga palleronii strain JS863 grew on 2,6-DNT as the sole source of carbon and nitrogen. The initial steps in the pathway for degradation of 2,6-DNT were determined by simultaneous induction, enzyme assays, and identification of metabolites through mass spectroscopy and nuclear magnetic resonance. 2,6-DNT was converted to 3-methyl-4-nitrocatechol by a dioxygenation reaction accompanied by the release of nitrite. 3-Methyl-4-nitrocatechol was the substrate for extradiol ring cleavage yielding 2-hydroxy-5-nitro-6-oxohepta-2,4-dienoic acid, which was converted to 2-hydroxy-5-nitropenta-2,4-dienoic acid. 2,4-DNT-degrading strains also converted 2,6-DNT to 3-methyl-4-nitrocatechol but did not metabolize the 3-methyl-4-nitrocatechol. Although 2,6-DNT prevented the degradation of 2,4-DNT by 2,4-DNT-degrading strains, the effect was not the result of inhibition of 2,4-DNT dioxygenase by 2,6-DNT or of 4-methyl-5-nitrocatechol monooxygenase by 3-methyl-4-nitrocatechol.     

Metabolism of the Aliphatic Nitramine 4-Nitro-2,4-Diazabutanal by Methylobacterium sp. Strain JS178

The aliphatic nitramine 4-nitro-2,4-diazabutanal (NDAB; C₂H₅N₃O₃) is a ring cleavage metabolite that accumulates during the aerobic degradation of the energetic compound hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) by various Rhodococcus spp. NDAB is also produced during the alkaline hydrolysis of either RDX or octahydro-1,3,5,7-tetranitro-1,3,5,7-tetrazocine (HMX) and during the photolysis of RDX. Traces of NDAB were observed in a soil sampled from an ammunition-manufacturing facility contaminated with both HMX and RDX, suggesting natural attenuation. In this study, we report the isolation of a soil bacterium that is able to degrade NDAB under aerobic conditions. The isolate is a pink-pigmented facultative methylotroph affiliated with the genus Methylobacterium. The strain, named Methylobacterium sp. strain JS178, degrades NDAB as a sole nitrogen source, with concomitant growth and formation of 1 molar equivalent of nitrous oxide (N₂O). Comparison of the growth yield of strain JS178 grown on NDAB, nitrite (NO₂⁻), or ammonium (NH₄⁺) as a nitrogen source revealed that 1 N equivalent is assimilated from each mole of NDAB, which completes the nitrogen mass balance. In radiotracer experiments, strain JS178 mineralized 1 C of the [¹⁴C]NDAB produced in situ from [¹⁴C]RDX by Rhodococcus sp. strain DN22. Studies on the regulation of NDAB degradation indicated that allantoin, an intermediate in the purine catabolic pathway and a central molecule in the storage and transport of nitrogen in plants, up-regulated the enzyme(s) involved in the degradation of the nitramine. The results reveal the potential for the sequential participation of rhodococci and methylobacteria to effect the complete degradation of RDX.     

Removal of the acetate-moiety of 2,4-dichlorophenoxyacetic acid in Ribes sativum

Ten minutes after uptake of 2,4-dichlorophenoxyacetic acid-1-¹⁴C(2,4-D-1-¹⁴C) by excised Ribes sativum leaves, 37·8 % of the radioactivity in water-soluble metabolites was in glyoxylic acid. When 2,4-D- 2-¹⁴C was supplied under the same conditions, 23·0 % of the radioactivity of the water-soluble rnetabolites was in glyoxylic acid. Radioactive glycine and glyoxylic acid, isolated from Ribes sativum 6 hr after uptake of 2,4-D-1-¹⁴C, contained essentially all of the ¹⁴C in the carboxyl-carbon atoms. When 2,4-D-2-¹⁴C was the precursor, the glycine isolated contained 64·8 % of its radioactivity in C₂, while 60·0 % of the radioactivity in glyoxylic acid was in C₂. The side-chain label of 2,4-D-2-¹⁴C-4-³⁶Cl was more efficiently incorporated into ethanol-insoluble plant residue than the ring-label. The metabolism of glyoxylic acid-1-¹⁴C and 2,4-D-1-¹⁴C in excised Ribes sativum leaves were compared. The data suggest a cleavage of the acetate-moiety of 2,4-D resulting in a C₂ compound, perhaps glyoxylate.     

Biotransformation of 2,4-dinitrotoluene in a phototrophic co-culture of engineered Synechococcus elongatus and Pseudomonas putida

In contrast to the current paradigm of using microbial mono-cultures in most biotechnological applications, increasing efforts are being directed towards engineering mixed-species consortia to perform functions that are difficult to programme into individual strains. In this work, we developed a synthetic microbial consortium composed of two genetically engineered microbes, a cyanobacterium (Synechococcus elongatus PCC 7942) and a heterotrophic bacterium (Pseudomonas putida EM173). These microbial species specialize in the co-culture: cyanobacteria fix CO₂ through photosynthetic metabolism and secrete sufficient carbohydrates to support the growth and active metabolism of P. putida, which has been engineered to consume sucrose and to degrade the environmental pollutant 2,4-dinitrotoluene (2,4-DNT). By encapsulating S. elongatus within a barium–alginate hydrogel, cyanobacterial cells were protected from the toxic effects of 2,4-DNT, enhancing the performance of the co-culture. The synthetic consortium was able to convert 2,4-DNT with light and CO₂ as key inputs, and its catalytic performance was stable over time. Furthermore, cycling this synthetic consortium through low nitrogen medium promoted the sucrose-dependent accumulation of polyhydroxyalkanoate, an added-value biopolymer, in the engineered P. putida strain. Altogether, the synthetic consortium displayed the capacity to remediate the industrial pollutant 2,4-DNT while simultaneously synthesizing biopolymers using light and CO₂ as the primary inputs.     

Photosynthesis of leaf cell protoplasts and permeability of the plasmalemma to some solutes

Photosynthesis was measured in mesophyll protoplasts isolated from spinach leaves. Under high intensity illumination and in the presence of 21% O₂, half-saturation of photosynthesis by CO₂ required CO₂ concentrations between 8 and 12 μm at different pH values of the suspending medium. Concentrations of HCO ₃ ^- needed for half-saturation increased correspondingly with the pH of the media. The pH profile of protoplast photosynthesis was much broader than that of CO₂ assimilation by isolated chloroplasts. The data indicate that leaf cells possess mechanisms to maintain considerable differences between external and internal pH over prolonged periods of time. Protoplast photosynthesis was inhibited by nitrite, acetate and bicarbonate; inhibition was more pronounced at low than at high pH and was attributed to stroma acidification. Nitrite was reduced in the light by protoplasts and chloroplasts. At pH 7.6, the apparent K_m NO ₂ ^- was about 0.6 mM for chloroplasts and 25 mM for protoplasts. Approximate permeability coefficients for NO ₂ ^- and HNO₂ were calculated from nitrite-dependent oxygen evolution at low nitrite concentrations, known nitrite or HNO₂ gradients, data on the surface area of protoplasts and chloroplasts and the pH profile of nitrite inhibition of photosynthesis. The membrane potential was assumed to be-100 mV. For the chloroplast envelope, permeability coefficients were 1.5·10^-3 ms^-1 (HNO₂) and 2·10^-8 ms^-1 (NO ₂ ^- ) and for the plasmalemma 4·10^-5 ms^-1 (HNO₂) and 5·10^-10 ms^-1 (NO ₂ ^- ). The values calculated for anion penetration probably represent upper limits of permeability. The protoplasts appeared to be largely impermeable to phosphate and phosphate esters. A rapid metabolic response of cells or cellular strands to added anionic substrates such as phosphate esters as reported in the literature appears to be possible only in damaged cells. It requires the presence of open channels between the cytosol and external medium.     

Tendency of using different aromatic compounds as substrates by 2,4-DNT dioxygenase expressed by pJS39 carrying the gene dntA from Burkholderia sp. strain DNT

The substrate range of 2,4-dinitrotoluene (DNT) dioxygenase was investigated by measuring substrate-dependent O₂ uptake and maximum growth (expressed in A₆₀₀) on substrate-containing minimal medium. The control for each strain had no added particular substrate. The following aromatic compounds: catechol, α-naphthalene acetic acid, β-dimethylaminobenzaldehyde, 3,4-dinitrosalicylic acid, p-nitrophenol, naphthanol, o-anisic acid, salicylic acid, toluene, and benzoic acid, were tried as possible substrates. Considering all substrates used, only p-nitrophenol showed zero oxygen uptake rate and zero growth. This indicates that it was rather unlikely that p-nitrophenol is a substrate analog for 2,4-DNT. Catechol was clearly used as a sole carbon source by both wild-type Escherichia. coli (JM103) and the dnt transformant (JS39). Using α-naphthalene acetic acid and β-dimethylaminobenzaldehyde as substrates resulted in DNT dioxygenase oxygen uptake rates of 11.8 and 14?μM/hr/mg protein, respectively. However, using both compounds as a carbon source, JS39 had twice the growth rate of E. coli JM103. For the remaining six substrates tested (3, 4-dinitrosalicylic acid, p-nitrophenol, o-anisic acid, salicylic acid, toluene, and benzoic acid), there appeared to be growth advantages for JS39 (even though the growth in the presence of substrate was less than the controls) suggesting a situation similar to that described for α-naphthalene and β-dimethylaminobenzaldehyde above. Combining results from our assay with respirometry and growth-based experiments will allow a better understanding of the biochemical consequences of these interactions. These results suggest that DNT dioxygenase gene, dntA carried by JS39, and those potential genes for substrates-degraded enzyme(s) system could have a common root.     

How does the cold stenothermal gadoid<Emphasis Type="Italic"> Lota lota</Emphasis> survive high water temperatures during summer?

The cold-stenothermal freshwater gadid Lota lota inhabiting the potamic regions of lowland rivers in central Europe, is exposed to summer temperatures up to 25 °C, which is far above the thermal preferendum of this species. Oxygen consumption rates, determined in field catches sampled at different times of the year, revealed that the basal metabolic rate is depressed during summer when water temperatures are high (152±16 mol O₂ 100 g^–1 h^–1at 22 °C in July compared to 250±33 mol O₂ 100 g^–1 h^–1 at 6 °C in November). This observation led us to investigate whether the observed depression of the metabolic rate is caused by oxygen limitation due to thermal impairment of the ventilatory system, as has been observed in other species. Determination of anaerobic end products (lactate and succinate) in the liver tissue of fish caught at different sampling dates did not show an accumulation of anaerobic end products during the summer, indicating no oxygen limitation. Measurements of enzyme activities in the white musculature and liver suggest that enzymes involved in aerobic metabolism were down-regulated during summer, which may have contributed to the observed reduction of metabolic rate.Abbreviations CS citric synthase - LDH lactate dehydrogenase - PK pyruvate kinase - TCA trichloroacetic acid Communicated by G. Heldmaier     

Microbial consortia that degrade 2,4-DNT by interspecies metabolism: isolation and characterisation

Two consortia, isolated by selective enrichment from a soil sample of anitroaromatic-contaminated site, degraded 2,4-DNT as their sole nitrogensource without accumulating one or more detectable intermediates. Thoughoriginating from the same sample, the optimised consortia had no commonmembers, indicating that selective enrichment resulted in different end points.Consortium 1 and consortium 2 contained four and six bacterial speciesrespectively, but both had two members that were able to collectivelydegrade 2,4-DNT. Variovorax paradoxus VM685 (consortium 1)and Pseudomonas sp. VM908 (consortium 2) initiate the catabolismof 2,4-DNT by an oxidation step, thereby releasing nitrite and forming4-methyl-5-nitrocatechol (4M5NC). Both strains contained a gene similarto the dntAa gene encoding 2,4-DNT dioxygenase. They subsequentlymetabolised 4M5NC to 2-hydroxy-5-methylquinone (2H5MQ) and nitrite,indicative of DntB or 4M5NC monooxygenase activity. A second consortiummember, Pseudomonas marginalis VM683 (consortium 1) and P.aeruginosa VM903, Sphingomonas sp. VM904, Stenotrophomonasmaltophilia VM905 or P. viridiflava VM907 (consortium 2), was foundto be indispensable for efficient growth of the consortia on 2,4-DNT and forefficient metabolisation of the intermediates 4M5NC and 2H5MQ. Knowledgeabout the interactions in this step of the degradation pathway is rather limited.In addition, both consortia can use 2,4-DNT as sole nitrogen and carbon source.A gene similar to the dntD gene of Burkholderia sp. strain DNT that catalyses ring fission was demonstrated by DNA hybridisation in the secondmember strains. To our knowledge, this is the first time that consortia are shownto be necessary for 2,4-DNT degradation.     

Mechanism of nitrite oxidation and oxidoreductase systems inNitrobacter agilis

Chemiosmotic coupling mechanisms operate in the electron transfer reactions from: nitrite to O₂, NO₂ ^– to NAD⁺, ascorbate to O₂, NADH to O₂, and NADH to NO₃ ^–. The enzyme systems catalyzing these reactions are named NO₂ ^–:O₂ oxidoreductase, ATP-dependent NO₂ ^–:NAD⁺ oxidoreductase, ascorbate:O₂ oxidoreductase, NADH:O₂ oxidoreductase, and NADH:NO₃ ^– oxidoreductase, respectively. All of the oxidoreduction reactions are exergonic with the exception of the ATP-dependent NO₂ ^–:NAD⁺ oxidoreductase system, which involves reversed electron flow against the thermodynamic gradients. The mechanism for nitrite oxidation was found to be quite different from that of ascorbate oxidation; both systems were insensitive, however, to rotenone, amytal, antimycin A, and 2-n-heptyl 4-hydroxyquinolineN-oxide. These compounds, on the other hand, severely inhibited the electron transfer reactions catalyzed by NADH:O₂ oxidoreductase, NADH:NO₃ ^– oxidoreductase, and the ATP-dependent NO₂ ^–:NAD⁺ oxidoreductase, indicating a common pathway of electron transport in these oxidoreductase systems. Cyanide inhibited all systems except the NADH:NO₃ ^– oxidoredctase. The uncoupler carbonyl cyanide-m-chlorophenyl hydrazone strongly inhibited NO₂ ^–:O₂ oxidoreductase and ATP-dependent NO₂ ^–:NAD⁺ oxidoreductase, which indicates the involvement of energy-linked reactions in both systems; the uncoupler caused a marked stimulation of the NADH:O₂ oxidoreductase and NADH:NO₃ ^– oxidoreductase without affecting the ascorbate:O₂ oxidoreductase activities.     

Reactive oxygen and nitrogen species’ effect on <Emphasis Type="Italic">lux</Emphasis>-biosensors based on <Emphasis Type="Italic">Escherichia coli</Emphasis> and <Emphasis Type="Italic">Salmonella typhimurium</Emphasis>

The effect of reactive oxygen and nitrogen species on lux-biosensors based on the Escherichia coli K12 MG1655 and Salmonella typhimurium LT2 host strains was investigated. The bioactivity of exogenous free radicals to the constitutively luminescent E. coli strain with plasmid pXen7 decreased in the order H₂O₂ > OCl^– > NO^? > RОO^? > ONOO^–> O₂^?- while the bioluminescence of S. typhimurium strain transformed with this plasmid decreased in the order NO^? > H₂O₂ > ONOO^– > RОO^? > OCl^– > O₂^?- The cross-reactivity of induced lux-biosensors to reactive oxygen and nitrogen species, the threshold sensitivity and the luminescence amplitude dependences from the plasmid specificity and the host strain were indicated. The biosensors with plasmid pSoxS′::lux possessed a wider range of sensitivity, including H₂O₂ and OCl^–, along with O₂^?- and NO^?. Among the used reactive oxygen and nitrogen species, H₂O₂ showed the highest induction activity concerning to the plasmids pKatG′::lux, pSoxS′::lux and pRecA′::lux. The inducible lux-biosensors based on S. typhimurium host strain possessed a higher sensitivity to the reactive oxygen and nitrogen species in comparison with the E. coli lux-biosensors.     

Microscale Distribution of Nitrification Activity in Sediment Determined with a Shielded Microsensor for Nitrate

Microprofiles of O₂ and NO₃^- were measured simultaneously in freshwater sediment with microsensors which were completely free from electrical interference because of coaxial designs. Depth profiles of nitrification (NO₃^- production) and denitrification (NO₃^- consumption) were subsequently determined by computer simulation of the measured microprofiles. The nitrifying bacterial community responded very quickly to changes in environmental conditions, and new steady-state microprofiles of O₂ and NO₃^- were usually approached within a few hours after perturbation. Nitrification started quickly after introduction of O₂ in previously anoxic layers, suggesting prolonged survival of the nitrifiers during anaerobiosis. Changes in the availability of O₂ and NH₄⁺ greatly affected the nitrification profile, and there was a high rate of coupled nitrification-denitrification under conditions in which nitrification occurred right above the oxic-anoxic interface. Addition of C₂H₂ rapidly removed the NO₃^- peaks, indicating that NO₃^- production was due mainly to autotrophic nitrification.     

Estimation of Nitrification and Denitrification from Microprofiles of Oxygen and Nitrate in Model Sediment Systems

The coupling between nitrification and denitrification and the regulation of these processes by oxygen were studied in freshwater sediment microcosms with O₂ and NO₃^- microsensors. Depth profiles of nitrification (indicated as NO₃^- production), denitrification (indicated as NO₃^- consumption), and O₂ consumption activities within the sediment were calculated from the measured concentration profiles. From the concentration profiles, it was furthermore possible to distinguish between the rate of denitrification based on the diffusional supply of NO₃^- from the overlying water and the rate based on NO₃^- supplied by benthic nitrification (D_w and D_n, respectively). An increase in O₂ concentration caused a deeper O₂ penetration while a decrease in D_w and an increase in D_n were observed. The relative importance for total denitrification of NO₃^- produced by nitrification thus increased compared with NO₃^- supplied from the water phase. The decrease in D_w at high oxygen was due to an increase in diffusion path for NO₃^- from the overlying water to the denitrifying layers in the anoxic sediment. At high O₂ concentrations, nitrifying activity was restricted to the lower part of the oxic zone where there was a continuous diffusional supply of NH₄⁺ from deeper mineralization processes, and the long diffusion path from the nitrification zone to the overlying water compared with the path to the denitrifying layers led to a stimulation in D_n.     

Ecotoxicity of 2,4-dinitrotoluene to cold tolerant plant species in a sub-Arctic soil

Abstract

Decades of live-fire training exercises have left millions of acres of military training lands contaminated with various munitions constituents such as dinitrotoluene. Those that pose a threat to higher organisms due to their toxicity and mobility in the soil are of particular concern. Plants aid in the biodegradation and phytoextraction of contaminants, and site-specific ecotoxicity determinations are critical to inform effective remediation strategy. These ecotoxicity determinations are lacking in cold-adapted plants and would be very informative for contaminated training lands in cold regions. Therefore, we conducted a phytotoxicity study to determine the median effective concentration (EC₅₀) of 2,4-dinitrotoluene (2,4-DNT) to four native Alaskan plant species in a sub-Arctic soil at two different temperatures. Plant species investigated were white spruce (Picea glauca), field locoweed (Oxytropis campestris), bluejoint grass (Calamagrostis canadensis), and Jacob’s ladder (Polemonium pulcherrimum). Seedling emergence, fresh plant mass, and dry plant mass were used to model plant response to 2,4-DNT contamination. White spruce was most tolerant to 2,4-DNT contamination (EC₅₀ = 130.8?mg kg^?1) and field locoweed was least tolerant (EC₅₀ = 0.38?mg kg^?1). In general, Arctic plant species were more vulnerable to 2,4-DNT when compared to plant types native to temperate or tropical regions.     

Degradation of n-Hexadecane and Its Metabolites by Pseudomonas aeruginosa under Microaerobic and Anaerobic Denitrifying Conditions

A strategy for sequential hydrocarbon bioremediation is proposed. The initial O₂-requiring transformation is effected by aerobic resting cells, thus avoiding a high oxygen demand. The oxygenated metabolites can then be degraded even under anaerobic conditions when supplemented with a highly water-soluble alternative electron acceptor, such as nitrate. To develop the new strategy, some phenomena were studied by examining Pseudomonas aeruginosa fermentation. The effects of dissolved oxygen (DO) concentration on n-hexadecane biodegradation were investigated first. Under microaerobic conditions, the denitrification rate decreased as the DO concentration decreased, implying that the O₂-requiring reactions were rate limiting. The effects of different nitrate and nitrite concentrations were examined next. When cultivated aerobically in tryptic soy broth supplemented with 0 to 0.35 g of NO₂⁻-N per liter, cells grew in all systems, but the lag phase was longer in the presence of higher nitrite concentrations. However, under anaerobic denitrifying conditions, even 0.1 g of NO₂⁻-N per liter totally inhibited cell growth. Growth was also inhibited by high nitrate concentrations (>1 g of NO₃⁻-N per liter). Cells were found to be more sensitive to nitrate or nitrite inhibition under denitrifying conditions than under aerobic conditions. Sequential hexadecane biodegradation by P. aeruginosa was then investigated. The initial fermentation was aerobic for cell growth and hydrocarbon oxidation to oxygenated metabolites, as confirmed by increasing dissolved total organic carbon (TOC) concentrations. The culture was then supplemented with nitrate and purged with nitrogen (N₂). Nitrate was consumed rapidly initially. The live cell concentration, however, also decreased. The aqueous-phase TOC level decreased by about 40% during the initial active period but remained high after this period. Additional experiments confirmed that only about one-half of the derived TOC was readily consumable under anaerobic denitrifying conditions.     

Intracellular nitrite accumulation: The cause of growth inhibition of Microcystis aeruginosa exposure to high nitrite level

The aim of the present study is to test the role of intracellular nitrite in external nitrite suppressing algal growth. We examined the growth of Microcystis aeruginosa at different nitrite levels under high nitrate conditions and without nitrate conditions. There were higher intracellular nitrite and lower P_m^chla, R_d ^chla, α^chl, maximum cell density and specific growth rate in high nitrate group than nitrate absence group at 5 mg NO₂^?‐N L^?1. At 10 and 15 mg NO₂^?‐N L^?1, P_m^chla, R_d ^chla, α^chl, maximum cell densities and specific growth rates in the high nitrate group became higher than those of the nitrate absence group, while a lower intracellular nitrite in the high nitrate group than nitrate absence group was observed. In addition, the intracellular nitrite and the growth of M. aeruginosa in the high nitrate group did not change from 5 to 10 mg NO₂^?‐N L^?1. In the nitrite uptake experiment, with nitrite concentration increasing from 5 to 15 mg NO₂^?‐N L^?1, maximum nitrite uptake rate of alga increased, and half‐saturation constant of alga decreased. These results indicate that external nitrite inhibited algal growth through stimulating intracellular nitrite rise, which resulted from overexpression of nitrite transporter.     

The effect of oxygen on nitrate and nitrite assimilation in leaves of Zea mays L. under dark conditions

The assimilation of nitrate under dark-N₂ and dark-O₂ conditions in Zea mays leaf tissue was investigated using colourimetric and ¹⁵N techniques for the determination of organic and inorganic nitrogen. Studies using ¹⁵N indicated that nitrate was assimilated under dark conditions. However, the rate of nitrate assimilation in the dark was only 28% of the rate under non-saturating light conditions. No nitrite accumulated under dark aerobiosis, even though nitrate reduction occurred under these conditions. The pattern of nitrite accumulation in leaf tissue in response to dark-N₂ conditions consisted of three phases: an initial lag phase, followed by a period of rapid nitrite accumulation and finally a phase during which the rate of nitrite accumulation declined. After a 1-h period of dark-anaerobiosis, both nitrate reduction and nitrite accumulation declined considerably. However, when O₂ was supplied, nitrate reduction was stimulated and the accumulated nitrite was rapidly reduced. Anaerobic conditions stimulated nitrate reduction in leaf tissue after a period of dark-aerobic pretreatment.