Microscale Biosensor for Measurement of Volatile Fatty Acids in Anoxic Environments

A microscale biosensor for acetate, propionate, isobutyrate, and lactate is described. The sensor is based on the bacterial respiration of low-molecular-weight, negatively charged species with a concomitant reduction of NO₃⁻ to N₂O. A culture of denitrifying bacteria deficient in N₂O reductase was immobilized in front of the tip of an electrochemical N₂O microsensor. The bacteria were separated from the outside environment by an ion-permeable membrane and supplied with nutrients (except for electron donors) from a medium reservoir behind the N₂O sensor. The signal of the sensor, which corresponded to the rate of N₂O production, was proportional to the supply of the electron donor to the bacterial mass. The selectivity for volatile fatty acids compared to other organic compounds was increased by selectively enhancing the transport of negatively charged compounds into the sensor by electrophoretic migration (electrophoretic sensitivity control). The sensor was susceptible to interference from O₂, N₂O, NO₂⁻, H₂S, and NO₃⁻. Interference from NO₃⁻ was low and could be quantified and accounted for. The detection limit was equivalent to about 1 μM acetate, and the 90% response time was 30 to 90 s. The response of the sensor was not affected by changes in pH between 5.5 and 9 and was also unaffected by changes in salinity in the range of 2 to 32‰. The functioning of the sensor over a temperature span of 7 to 30°C was investigated. The concentration range for a linear response was increased five times by increasing the temperature from 7 to 19.5°C. The life span of the biosensor varied between 1 and 3 weeks after manufacturing.     

Dissimilatory Reduction of NO2− to NH4+ and N2O by a Soil Citrobacter sp.

Dissimilatory reduction of NO₂⁻ to N₂O and NH₄⁺ by a soil Citrobacter sp. was studied in an attempt to elucidate the physiological and ecological significance of N₂O production by this mechanism. In batch cultures with defined media, NO₂⁻ reduction to NH₄⁺ was favored by high glucose and low NO₃⁻ concentrations. Nitrous oxide production was greatest at high glucose and intermediate NO₃⁻ concentrations. With succinate as the energy source, little or no NO₂⁻ was reduced to NH₄⁺ but N₂O was produced. Resting cell suspensions reduced NO₂⁻ simultaneously to N₂O and free extracellular NH₄⁺. Chloramphenicol prevented the induction of N₂O-producing activity. The K_m for NO₂⁻ reduction to N₂O was estimated to be 0.9 mM NO₂⁻, yet the apparent K_m for overall NO₂⁻ reduction was considerably lower, no greater than 0.04 mM NO₂⁻. Activities for N₂O and NH₄⁺ production increased markedly after depletion of NO₃⁻ from the media. Amendment with NO₃⁻ inhibited N₂O and NH₄⁺ production by molybdate-grown cells but not by tungstate-grown cells. Sulfite inhibited production of NH₄⁺ but not of N₂O. In a related experiment, three Escherichia coli mutants lacking NADH-dependent nitrite reductase produced N₂O at rates equal to the wild type. These observations suggest that N₂O is produced enzymatically but not by the same enzyme system responsible for dissimilatory reduction of NO₂⁻ to NH₄⁺.     

Novel Denitrifying Bacterium Ochrobactrum anthropi YD50.2 Tolerates High Levels of Reactive Nitrogen Oxides

Most studies of bacterial denitrification have used nitrate (NO₃⁻) as the first electron acceptor, whereas relatively less is understood about nitrite (NO₂⁻) denitrification. We isolated novel bacteria that proliferated in the presence of high levels of NO₂⁻ (72 mM). Strain YD50.2, among several isolates, was taxonomically positioned within the α subclass of Proteobacteria and identified as Ochrobactrum anthropi YD50.2. This strain denitrified NO₂⁻, as well as NO₃⁻. The gene clusters for denitrification (nar, nir, nor, and nos) were cloned from O. anthropi YD50.2, in which the nir and nor operons were linked. We confirmed that nirK in the nir-nor operon produced a functional NO₂⁻ reductase containing copper that was involved in bacterial NO₂⁻ reduction. The strain denitrified up to 40 mM NO₂⁻ to dinitrogen under anaerobic conditions in which other denitrifiers or NO₃⁻ reducers such as Pseudomonas aeruginosa and Ralstonia eutropha and nitrate-respiring Escherichia coli neither proliferated nor reduced NO₂⁻. Under nondenitrifying aerobic conditions, O. anthropi YD50.2 and its type strain ATCC 49188^T proliferated even in the presence of higher levels of NO₂⁻ (100 mM), and both were considerably more resistant to acidic NO₂⁻ than were the other strains noted above. These results indicated that O. anthropi YD50.2 is a novel denitrifier that has evolved reactive nitrogen oxide tolerance mechanisms.Environmental bacteria maintain the global nitrogen cycle by metabolizing organic and inorganic nitrogen compounds. Denitrification is critical for maintenance of the global nitrogen cycle, through which nitrate (NO₃⁻) or nitrite (NO₂⁻) is reduced to gaseous nitrogen forms such as N₂ and nitrous oxide (N₂O) (19, 47). Decades of investigations into denitrifying bacteria have revealed their ecological impact (9), their molecular mechanisms of denitrification (13, 25, 47), and the industrial importance of removing nitrogenous contaminants from wastewater (31, 36). Bacterial denitrification is considered to comprise four successive reduction steps, each of which is catalyzed by NO₃⁻ reductase (Nar), NO₂⁻ reductase (Nir), nitric oxide (NO) reductase (Nor), and N₂O reductase (Nos). The reaction of each enzyme is linked to the electron transport chain on the cellular membrane and accompanies oxidative phosphorylation, implying that bacterial denitrification is of as much physiological significance as anaerobic respiration (25, 47). Most denitrifying bacteria are facultative anaerobes and respire with oxygen under aerobic conditions. Because denitrification is induced in the absence of oxygen, it is considered an alternative mechanism of energy conservation that has evolved as an adaptation to anaerobic circumstances (13, 47).Nitrite and NO are hazardous to bacteria, since they generate highly reactive nitrogen species (RNS) under physiological conditions and damage cellular DNA, lipid, and proteins (28, 37). Denitrifying bacteria are thought to be threatened by RNS since they reduce NO₃⁻ to generate NO₂⁻ and NO as denitrifying intermediates. Furthermore, denitrifying bacteria often inhabit environments where they are exposed to NO₂⁻ and NO and hence high levels of RNS. Recent reports suggest that pathogenic bacteria invading animal tissues are attacked by NO generated by macrophages (12). Such bacteria involve denitrifiers, and some of them, for example, Neisseria meningitidis (1) and Pseudomonas aeruginosa, acquire resistance to NO by producing Nor (44). The utilization (reduction) of NO by Brucella increases the survival of infected mice (2). These examples suggest that production of a denitrifying mechanism affects bacterial survival of threats from both endogenous and extracellular RNS. However, the mechanism of RNS tolerance induced by denitrifying bacteria is not fully understood.Ubiquitous gram-negative Ochrobactrum strains are widely distributed in soils and aqueous environments, where they biodegrade aromatic compounds (11), organophosphorus pesticides (45), and other hydrocarbons (38) and remove heavy metal ions such as chromium and cadmium (24). Having been isolated from clinical specimens, Ochrobactrum anthropi is currently recognized as an emerging opportunistic pathogen, although relatively little is known about its pathogenesis and factors contributing to its virulence (7, 30). Manipulation systems have been developed to investigate these issues at the molecular genetic level (33). Some O. anthropi strains have been identified as denitrifiers (21), although the denitrifying properties of these strains have not been investigated in detail. This study was undertaken to examine the denitrifying properties of O. anthropi in more detail. O. anthropi YD50.2 was selected for this study and was isolated herein. The strain denitrified high levels of NO₂⁻ (up to 40 mM) to dinitrogen under anaerobic conditions. The strain was highly resistant to acidified NO₂⁻ under nondenitrifying aerobic conditions. These results indicate that O. anthropi YD50.2 has mechanisms that produce tolerance to RNS.     

Denitrification in San Francisco Bay Intertidal Sediments

The acetylene block technique was employed to study denitrification in intertidal estuarine sediments. Addition of nitrate to sediment slurries stimulated denitrification. During the dry season, sediment-slurry denitrification rates displayed Michaelis-Menten kinetics, and ambient NO₃⁻ + NO₂⁻ concentrations (≤26 μM) were below the apparent K_m (50 μM) for nitrate. During the rainy season, when ambient NO₃⁻ + NO₂⁻ concentrations were higher (37 to 89 μM), an accurate estimate of the K_m could not be obtained. Endogenous denitrification activity was confined to the upper 3 cm of the sediment column. However, the addition of nitrate to deeper sediments demonstrated immediate N₂O production, and potential activity existed at all depths sampled (the deepest was 15 cm). Loss of N₂O in the presence of C₂H₂ was sometimes observed during these short-term sediment incubations. Experiments with sediment slurries and washed cell suspensions of a marine pseudomonad confirmed that this N₂O loss was caused by incomplete blockage of N₂O reductase by C₂H₂ at low nitrate concentrations. Areal estimates of denitrification (in the absence of added nitrate) ranged from 0.8 to 1.2 μmol of N₂ m⁻² h⁻¹ (for undisturbed sediments) to 17 to 280 μmol of N₂ m⁻² h⁻¹ (for shaken sediment slurries).     

Early effects of salinity on nitrate assimilation in barley seedlings

The effect of NaCl and Na₂SO₄ salinity on NO₃⁻ assimilation in young barley (Hordeum vulgare L. var Numar) seedlings was studied. The induction of the NO₃⁻ transporter was affected very little; the major effect of the salts was on its activity. Both Cl⁻ and SO₄²⁻ salts severely inhibited uptake of NO₃⁻. When compared on the basis of osmolality of the uptake solutions, Cl⁻ salts were more inhibitory (15-30%) than SO₄²⁻ salts. At equal concentrations, SO₄²⁻ salts inhibited NO₃⁻ uptake 30 to 40% more than did Cl⁻ salts. The absolute concentrations of each ion seemed more important as inhibitors of NO₃⁻ uptake than did the osmolality of the uptake solutions. Both K⁺ and Na⁺ salts inhibited NO₃⁻ uptake similarly; hence, the process seemed more sensitive to anionic salinity than to cationic salinity.

Unlike NO₃⁻ uptake, NO₃⁻ reduction was not affected by salinity in short-term studies (12 hours). The rate of reduction of endogenous NO₃⁻ in leaves of seedlings grown on NaCl for 8 days decreased only 25%. Nitrate reductase activity in the salt-treated leaves also decreased 20% but its activity, determined either in vitro or by the `anaerobic' in vivo assay, was always greater than the actual in situ rate of NO₃⁻ reduction. When salts were added to the assay medium, the in vitro enzymic activity was severely inhibited; whereas the anaerobic in vivo nitrate reductase activity was affected only slightly. These results indicate that in situ nitrate reductase activity is protected from salt injury. The susceptibility to injury of the NO₃⁻ transporter, rather than that of the NO₃⁻ reduction system, may be a critical factor to plant survival during salt stress.

     

Eukaryotic nirK Genes Encoding Copper-Containing Nitrite Reductase: Originating from the Protomitochondrion?

Although denitrification or nitrate respiration has been found among a few eukaryotes, its phylogenetic relationship with the bacterial system remains unclear because orthologous genes involved in the bacterial denitrification system were not identified in these eukaryotes. In this study, we isolated a gene from the denitrifying fungus Fusarium oxysporum that is homologous to the bacterial nirK gene responsible for encoding copper-containing nitrite reductase (NirK). Characterization of the gene and its recombinant protein showed that the fungal nirK gene is the first eukaryotic ortholog of the bacterial counterpart involved in denitrification. Additionally, recent genome analyses have revealed the occurrence of nirK homologs in many fungi and protozoa, although the denitrifying activity of these eukaryotes has never been examined. These eukaryotic homolog genes, together with the fungal nirK gene of F. oxysporum, are grouped in the same branch of the phylogenetic tree as the nirK genes of bacteria, archaea, and eukaryotes, implying that eukaryotic nirK and its homologs evolved from a single ancestor (possibly the protomitochondrion). These results show that the fungal denitrifying system has the same origin as its bacterial counterpart.Denitrification plays an important role in the global nitrogen cycle and reduces nitrate (NO₃⁻) and/or nitrite (NO₂⁻) to a gaseous form of nitrogen, generally to dinitrogen (N₂) or nitrous oxide (N₂O) (27). It typically follows four reduction stages, NO₃⁻ → NO₂⁻ → NO → N₂O → N₂, each of which is catalyzed by a specific reductase: dissimilatory NO₃⁻ reductase (dNaR), dissimilatory NO₂⁻ reductase (dNiR), nitric oxide (NO) reductase (NoR), and N₂O reductase, respectively. These enzymes receive electrons from a respiratory chain functioning as a “terminal reductase.” Thus, denitrification exhibits a physiological significance in its ability to anaerobically respire through the processes of nitrate respiration, nitrite respiration, and so forth. Denitrification was previously thought to be a characteristic of bacteria; however, similar reactions have been found to occur in a few eukaryotes and archaea (6, 27). Eukaryotic nitrate respiration was first found in protozoa that reside in an anaerobic freshwater habitat (8). The organism particularly reduces NO₃⁻ to NO₂⁻ in a single step, a process which recovers dNaR activity in the mitochondrial fraction but does not result in denitrification. Eukaryotic denitrification was first found to occur among fungi (19, 20), which generally form N₂O from NO₃⁻ or NO₂⁻. Recently, eukaryotic denitrification was also found in a benthic foraminifer that forms N₂ from NO₃⁻ (18). The fungal denitrification system localizes in the mitochondria and couples to the mitochondrial electron transport chain to produce ATP (12, 21), thus exhibiting properties similar to those of the bacterial systems in its ability to respire anaerobically. Moreover, the mechanism of anaerobic respiration in the “aerobic” organelle of eukaryotes (mitochondrion) evokes interest regarding the origin and evolution of the mitochondrion.The main components of the fungal denitrifying system, the dNaR, dNiR, and NoR proteins, were either completely or partially purified from Fusarium oxysporum. Fungal NoR of the cytochrome P450 (P450) type, referred to as P450nor (CYP55) (11, 16), is a distinct species of bacterial cytochrome cb-type NoR. By contrast, the previously isolated fungal dNiR protein is a copper-containing type (NirK) that closely resembles its bacterial counterpart (13). Furthermore, dNaR activity partially purified from the mitochondrial membrane fraction showed that fungal dNaR possibly resembles its bacterial counterpart, NarGHI (12, 23). Therefore, while a portion of the fungal system appears to resemble its bacterial counterpart, the phylogenetic relationship between the fungal and bacterial denitrification systems remained unclear because the genes of the fungal components (dNaR and dNiR) have not been sequenced.Recent genome analyses have revealed the presence of nirK homolog genes in many eukaryotes (fungi and protozoa), a finding consistent with our previous findings on the isolation of the fungal NirK protein (13). Therefore, whether these eukaryotes containing the nirK homolog gene exhibit denitrification activity and whether the denitrifying fungus F. oxysporum really contains a nirK gene deserve a great deal of attention. To address this issue, we used the suppression subtractive hybridization (SSH) technique (7) and succeeded in isolating the nirK gene from the denitrifying fungus F. oxysporum.     

Anaerobic Growth and Denitrification among Different Serogroups of Soybean Rhizobia

We screened soybean rhizobia originating from three germplasm collections for the ability to grow anaerobically in the presence of NO₃⁻ and for differences in final product formation from anaerobic NO₃⁻ metabolism. Denitrification abilities of selected strains as free-living bacteria and as bacteroids were compared. Anaerobic growth in the presence of NO₃⁻ was observed in 270 of 321 strains of soybean rhizobia. All strains belonging to the 135 serogroup did not grow anaerobically in the presence of NO₃⁻. An investigation with several strains indicated that bacteria not growing anaerobically in the presence of NO₃⁻ also did not utilize NO₃⁻ as the sole N source aerobically. An exception was strain USDA 33, which grew on NO₃⁻ but failed to denitrify. Dissimilation of NO₃⁻ by the free-living cultures proceeded without the significant release of intermediate products. Nitrous oxide reductase was inhibited by C₂H₂, but preceding steps of denitrification were not affected. Final products of denitrification were NO₂⁻, N₂O, or N₂; serogroups 31, 46, 76, and 94 predominantly liberated NO₂⁻, whereas evolution of N₂ was prevalent in serogroups 110 and 122, and all three were formed as final products by strains belonging to serogroups 6 and 123. Anaerobic metabolism of NO₃⁻ by bacteroid preparations of Bradyrhizobium japonicum proceeded without delay and was evident by NO₂⁻ accumulation irrespective of which final product was formed by the strain as free-living bacteria. Anaerobic C₂H₂ reduction in the presence of NO₃⁻ was observed in bacteroid preparations capable of NO₃⁻ respiration but was absent in bacteria that were determined to be deficient in dissimilatory nitrate reductase.     

High rates of denitrification and nitrous oxide emission in arid biological soil crusts from the Sultanate of Oman

Using a combination of process rate determination, microsensor profiling and molecular techniques, we demonstrated that denitrification, and not anaerobic ammonium oxidation (anammox), is the major nitrogen loss process in biological soil crusts from Oman. Potential denitrification rates were 584±101 and 58±20 μmol N m⁻² h⁻¹ for cyanobacterial and lichen crust, respectively. Complete denitrification to N₂ was further confirmed by an ¹⁵NO₃⁻ tracer experiment with intact crust pieces that proceeded at rates of 103±19 and 27±8 μmol N m⁻² h⁻¹ for cyanobacterial and lichen crust, respectively. Strikingly, N₂O gas was emitted at very high potential rates of 387±143 and 31±6 μmol N m⁻² h⁻¹ from the cyanobacterial and lichen crust, respectively, with N₂O accounting for 53–66% of the total emission of nitrogenous gases. Microsensor measurements revealed that N₂O was produced in the anoxic layer and thus apparently originated from incomplete denitrification. Using quantitative PCR, denitrification genes were detected in both the crusts and were expressed either in comparable (nirS) or slightly higher (narG) numbers in the cyanobacterial crusts. Although 99% of the nirS sequences in the cyanobacterial crust were affiliated to an uncultured denitrifying bacterium, 94% of these sequences were most closely affiliated to Paracoccus denitrificans in the lichen crust. Sequences of nosZ gene formed a distinct cluster that did not branch with known denitrifying bacteria. Our results demonstrate that nitrogen loss via denitrification is a dominant process in crusts from Oman, which leads to N₂O gas emission and potentially reduces desert soil fertility.     

Kinetics of Denitrifying Growth by Fast-Growing Cowpea Rhizobia

Two fast-growing strains of cowpea rhizobia (A26 and A28) were found to grow anaerobically at the expense of NO₃⁻, NO₂⁻, and N₂O as terminal electron acceptors. The two major differences between aerobic and denitrifying growth were lower yield coefficients (Y) and higher saturation constants (K_s) with nitrogenous oxides as electron acceptors. When grown aerobically, A26 and A28 adhered to Monod kinetics, respectively, as follows: K_s, 3.4 and 3.8 μM; Y, 16.0 and 14.0 g · cells eq⁻¹; μ_max, 0.41 and 0.33 h⁻¹. Yield coefficients for denitrifying growth ranged from 40 to 70% of those for aerobic growth. Only A26 adhered to Monod kinetics with respect to growth on all three nitrogenous oxides. The apparent K_s values were 41, 270, and 460 μM for nitrous oxide, nitrate, and nitrite, respectively; the K_s for A28 grown on nitrate was 250 μM. The results are kinetically and thermodynamically consistent in explaining why O₂ is the preferred electron acceptor. Although no definitive conclusions could be drawn regarding preferential utilization of nitrogenous oxides, nitrite was inhibitory to both strains and effected slower growth. However, growth rates were identical (μ_max, 0.41 h⁻¹) when A26 was grown with either O₂ or NO₃⁻ as an electron acceptor and were only slightly reduced when A28 was grown with NO₃⁻ (0.25 h⁻¹) as opposed to O₂ (0.33 h⁻¹).     

Sub-Parts-Per-Billion Nitrate Method: Use of an N2O-Producing Denitrifier to Convert NO3− or 15NO3− to N2O

A more sensitive analytical method for NO₃⁻ was developed based on the conversion of NO₃⁻ to N₂O by a denitrifier that could not reduce N₂O further. The improved detectability resulted from the high sensitivity of the ⁶³Ni electron capture gas chromatographic detector for N₂O and the purification of the nitrogen afforded by the transformation of the N to a gaseous product with a low atmospheric background. The selected denitrifier quantitatively converted NO₃⁻ to N₂O within 10 min. The optimum measurement range was from 0.5 to 50 ppb (50 μg/liter) of NO₃⁻ N, and the detection limit was 0.2 ppb of N. The values measured by the denitrifier method compared well with those measured by the high-pressure liquid chromatographic UV method above 2 ppb of N, which is the detection limit of the latter method. It should be possible to analyze all types of samples for nitrate, except those with inhibiting substances, by this method. To illustrate the use of the denitrifier method, NO₃⁻ concentrations of <2 ppb of NO₃⁻ N were measured in distilled and deionized purified water samples and in anaerobic lake water samples, but were not detected at the surface of the sediment. The denitrifier method was also used to measure the atom% of ¹⁵N in NO₃⁻. This method avoids the incomplete reduction and contamination of the NO₃⁻ -N by the NH₄⁺ and N₂ pools which can occur by the conventional method of ¹⁵NO₃⁻ analysis. N₂O-producing denitrifier strains were also used to measure the apparent K_m values for NO₃⁻ use by these organisms. Analysis of N₂O production by use of a progress curve yielded K_m values of 1.7 and 1.8 μM NO₃⁻ for the two denitrifier strains studied.     

Aerobic nitrous oxide production through N-nitrosating hybrid formation in ammonia-oxidizing archaea

Soil emissions are largely responsible for the increase of the potent greenhouse gas nitrous oxide (N₂O) in the atmosphere and are generally attributed to the activity of nitrifying and denitrifying bacteria. However, the contribution of the recently discovered ammonia-oxidizing archaea (AOA) to N₂O production from soil is unclear as is the mechanism by which they produce it. Here we investigate the potential of Nitrososphaera viennensis, the first pure culture of AOA from soil, to produce N₂O and compare its activity with that of a marine AOA and an ammonia-oxidizing bacterium (AOB) from soil. N. viennensis produced N₂O at a maximum yield of 0.09% N₂O per molecule of nitrite under oxic growth conditions. N₂O production rates of 4.6±0.6 amol N₂O cell⁻¹ h⁻¹ and nitrification rates of 2.6±0.5 fmol NO₂⁻ cell⁻¹ h⁻¹ were in the same range as those of the AOB Nitrosospira multiformis and the marine AOA Nitrosopumilus maritimus grown under comparable conditions. In contrast to AOB, however, N₂O production of the two archaeal strains did not increase when the oxygen concentration was reduced, suggesting that they are not capable of denitrification. In ¹⁵N-labeling experiments we provide evidence that both ammonium and nitrite contribute equally via hybrid N₂O formation to the N₂O produced by N. viennensis under all conditions tested. Our results suggest that archaea may contribute to N₂O production in terrestrial ecosystems, however, they are not capable of nitrifier-denitrification and thus do not produce increasing amounts of the greenhouse gas when oxygen becomes limiting.     

Denitrification and Assimilatory Nitrate Reduction in Aquaspirillum magnetotacticum

Aquaspirillum magnetotacticum MS-1 grew microaerobically but not anaerobically with NO₃⁻ or NH₄⁺ as the sole nitrogen source. Nevertheless, cell yields varied directly with NO₃⁻ concentration under microaerobic conditions. Products of NO₃⁻ reduction included NH₄⁺, N₂O, NO, and N₂. NO₂⁻ and NH₂OH, each toxic to cells at 0.2 mM, were not detected as products of cells growing on NO₃⁻. NO₃⁻ reduction to NH₄⁺ was completely repressed by the addition of 2 mM NH₄⁺ to the growth medium, whereas NO₃⁻ reduction to N₂O or to N₂ was not. C₂H₂ completely inhibited N₂O reduction to N₂ by growing cells. These results indicate that A. magnetotacticum is a microaerophilic denitrifier that is versatile in its nitrogen metabolism, concomitantly reducing NO₃⁻ by assimilatory and dissimilatory means. This bacterium appears to be the first described denitrifier with an absolute requirement for O₂. The process of NO₃⁻ reduction appears well adapted for avoiding accumulation of several nitrogenous intermediates that are toxic to cells.     

Ecology of Thioploca spp.: Nitrate and Sulfur Storage in Relation to Chemical Microgradients and Influence of Thioploca spp. on the Sedimentary Nitrogen Cycle

Microsensors, including a recently developed NO₃⁻ biosensor, were applied to measure O₂ and NO₃⁻ profiles in marine sediments from the upwelling area off central Chile and to investigate the influence of Thioploca spp. on the sedimentary nitrogen metabolism. The studies were performed in undisturbed sediment cores incubated in a small laboratory flume to simulate the environmental conditions of low O₂, high NO₃⁻, and bottom water current. On addition of NO₃⁻ and NO₂⁻, Thioploca spp. exhibited positive chemotaxis and stretched out of the sediment into the flume water. In a core densely populated with Thioploca, the penetration depth of NO₃⁻ was only 0.5 mm and a sharp maximum of NO₃⁻ uptake was observed 0.5 mm above the sediment surface. In sediments with only few Thioploca spp., NO₃⁻ was detectable down to a depth of 2 mm and the maximum consumption rates were observed within the sediment. No chemotaxis toward nitrous oxide (N₂O) was observed, which is consistent with the observation that Thioploca does not denitrify but reduces intracellular NO₃⁻ to NH₄⁺. Measurements of the intracellular NO₃⁻ and S⁰ pools in Thioploca filaments from various depths in the sediment gave insights into possible differences in the migration behavior between the different species. Living filaments containing significant amounts of intracellular NO₃⁻ were found to a depth of at least 13 cm, providing final proof for the vertical shuttling of Thioploca spp. and nitrate transport into the sediment.     

Denitrification by Chromobacterium violaceum

One host (Rana catesbiana)-associated and two free-living mesophilic strains of bacteria with violet pigmentation and biochemical characteristics of Chromobacterium violaceum were isolated from freshwater habitats. Cells of each freshly isolated strain and of strain ATCC 12472 (the neotype strain) grew anaerobically with glucose as the sole carbon and energy source. The major fermentation products of cells grown in Trypticase soy broth (BBL Microbiology Systems, Cockeysville, Md.) supplemented with glucose included acetate, small amounts of propionate, lactate, and pyruvate. The final cell yield and culture growth rate of each strain cultured anaerobically in this medium increased approximately twofold with the addition of 2 mM NaNO₃. Final growth yields increased in direct proportion to the quantity of added NaNO₃ over the range of 0.5 to 5 mM. Each strain reduced NO₃⁻, producing NO₂⁻, NO, and N₂O. NO₂⁻ accumulated transiently. With 2 mM NaNO₃ in the medium, N₂O made up 85 to 98% of the N product recovered with each strain. N-oxides were recovered in the same quantity and distribution whether 0.01 atm (ca. 1 kPa) of C₂H₂ (added to block N₂O reduction) was present or not. Neither N₂ production nor gas accumulation was detected during NO₃⁻ reduction by growing cells. Cell growth in media containing 0.5 to 5 mM NaNO₂ in lieu of NaNO₃ was delayed, and although N₂O was produced by the end of growth, NO₂⁻ -containing media did not support growth to an extent greater than did medium lacking NO₃⁻ or NO₂⁻. The data indicate that C. violaceum cells ferment glucose or denitrify, terminating denitrification with the production of N₂O, and that NO₂⁻ reduction to N₂O is not coupled to growth but may serve as a detoxification mechanism. No strain detectably fixed N₂ (reduced C₂H₂).     

Adaptation of Denitrifying Populations to Low Soil pH

Natural denitrification rates and activities of denitrifying enzymes were measured in an agricultural soil which had a 20-year past history of low pH (pH ca. 4) due to fertilization with acid-generating ammonium salts. The soil adjacent to this site had been limed and had a pH of ca. 6.0. Natural denitrification rates of these areas were of similar magnitude: 158 ng of N g⁻¹ of soil day⁻¹ for the acid soil and 390 ng of N g⁻¹ of soil day⁻¹ at the neutral site. Estimates of in situ denitrifying enzyme activity were higher in the neutral soil, but substantial enzyme activity was also detected in the acid soil. Rates of nitrous oxide reduction were very low, even when NO₃⁻ and NO₂⁻ were undetectable, and were ca. 400 times lower than the rates of N₂O production from NO₃⁻. Denitrification rates measured in slurries of the acid and neutral soil showed distinctly different pH optima (pH 3.9 and pH 6.3) which were near the pH values of the two soils. This suggests that an acid-tolerant denitrifying population had been selected during the 20-year period of low pH.     

Production of NO2- and N2O by Nitrifying Bacteria at Reduced Concentrations of Oxygen

Pure cultures of the marine ammonium-oxidizing bacterium Nitrosomonas sp. were grown in the laboratory at oxygen partial pressures between 0.005 and 0.2 atm (0.18 to 7 mg/liter). Low oxygen conditions induced a marked decrease in the rate for production of NO₂^-, from 3.6 × 10⁻¹⁰ to 0.5 × 10⁻¹⁰ mmol of NO₂^- per cell per day. In contrast, evolution of N₂O increased from 1 × 10⁻¹² to 4.3 × 10⁻¹² mmol of N per cell per day. The yield of N₂O relative to NO₂^- increased from 0.3% to nearly 10% (moles of N in N₂O per mole of NO₂^-) as the oxygen level was reduced, although bacterial growth rates changed by less than 30%. Nitrifying bacteria from the genera Nitrosomonas, Nitrosolobus, Nitrosospira, and Nitrosococcus exhibited similar yields of N₂O at atmospheric oxygen levels. Nitrite-oxidizing bacteria (Nitrobacter sp.) and the dinoflagellate Exuviaella sp. did not produce detectable quantities of N₂O during growth. The results support the view that nitrification is an important source of N₂O in the environment.     

Microzonation of Denitrification Activity in Stream Sediments as Studied with a Combined Oxygen and Nitrous Oxide Microsensor

Microzonation of denitrification was studied in stream sediments by a combined O₂ and N₂O microsensor technique. O₂ and N₂O concentration profiles were recorded simultaneously in intact sediment cores in which C₂H₂ was added to inhibit N₂O reduction in denitrification. The N₂O profiles were used to obtain high-resolution profiles of denitrification activity and NO₃⁻ distribution in the sediments. O₂ penetrated about 1 mm into the dark-incubated sediments, and denitrification was largely restricted to a thin anoxic layer immediately below that. With 115 μM NO₃⁻ in the water phase, denitrification was limited to a narrow zone from 0.7 to 1.4 mm in depth, and total activity was 34 nmol of N cm⁻² h⁻¹. With 1,250 μM NO₃⁻ in the water, the denitrification zone was extended to a layer from 0.9 to 4.8 mm in depth, and total activity increased to 124 nmol of N cm⁻² h⁻¹. Within most of the activity zone, denitrification was not dependent on the NO₃⁻ concentration and the apparent K_m for NO₃⁻ was less than 10 μM. Denitrification was the only NO₃⁻-consuming process in the dark-incubated stream sediment. Even in the presence of C₂H₂, a significant N₂O reduction (up to 30% of the total N₂O production) occurred in the reduced, NO₃⁻-free layers below the denitrification zone. This effect must be corrected for during use of the conventional C₂H₂ inhibition technique.     

Chemical and Biological Interactions during Nitrate and Goethite Reduction by Shewanella putrefaciens 200

Although previous research has demonstrated that NO₃⁻ inhibits microbial Fe(III) reduction in laboratory cultures and natural sediments, the mechanisms of this inhibition have not been fully studied in an environmentally relevant medium that utilizes solid-phase, iron oxide minerals as a Fe(III) source. To study the dynamics of Fe and NO₃⁻ biogeochemistry when ferric (hydr)oxides are used as the Fe(III) source, Shewanella putrefaciens 200 was incubated under anoxic conditions in a low-ionic-strength, artificial groundwater medium with various amounts of NO₃⁻ and synthetic, high-surface-area goethite. Results showed that the presence of NO₃⁻ inhibited microbial goethite reduction more severely than it inhibited microbial reduction of the aqueous or microcrystalline sources of Fe(III) used in other studies. More interestingly, the presence of goethite also resulted in a twofold decrease in the rate of NO₃⁻ reduction, a 10-fold decrease in the rate of NO₂⁻ reduction, and a 20-fold increase in the amounts of N₂O produced. Nitrogen stable isotope experiments that utilized δ¹⁵N values of N₂O to distinguish between chemical and biological reduction of NO₂⁻ revealed that the N₂O produced during NO₂⁻ or NO₃⁻ reduction in the presence of goethite was primarily of abiotic origin. These results indicate that concomitant microbial Fe(III) and NO₃⁻ reduction produces NO₂⁻ and Fe(II), which then abiotically react to reduce NO₂⁻ to N₂O with the subsequent oxidation of Fe(II) to Fe(III).     

Combined Oxygen and Nitrous Oxide Microsensor for Denitrification Studies

The construction of a microsensor which can be used to measure O₂ and N₂O simultaneously is described. The microsensor exhibited a linear response to both O₂ and N₂O, and the response to N₂O was independent of the O₂ concentration and vice versa. The N₂O detection limit of a microsensor with a tip diameter of 20 μm was around 1 μmol liter⁻¹. The signals for O₂ and N₂O were affected by hydrogen sulfide, but other interfering agents were not observed in the biofilms and sediments analyzed. Microprofiles of O₂ and N₂O were measured in a biofilm which was exposed to acetylene to block the N₂O reductase activity of denitrifying bacteria. O₂ penetrated about 0.5 mm into the biofilm and was not affected by acetylene, but the N₂O concentration at 1.4 mm depth increased from 32 to 411 μmol liter⁻¹ after the addition of the inhibitor. The shape of the N₂O profile after the addition of acetylene showed that denitrification (denitrifying activity) was detectable in all anoxic layers of the biofilm.