Root Nodule Enzymes of Ammonia Assimilation in Alfalfa (Medicago sativa L.) : DEVELOPMENTAL PATTERNS AND RESPONSE TO APPLIED NITROGEN

Nitrogenase-dependent acetylene reduction activity of glasshouse-grown alfalfa (Medicago sativa L.) decreased rapidly in response both to harvesting (80% shoot removal) and applied NO₃⁻ at 40 and 80 kilograms N per hectare. Acetylene reduction activity of harvested plants grown on 0 kilogram N per hectare began to recover by day 15 as shoot regrowth became significant. In contrast, acetylene reduction activity of all plants treated with 80 kilograms NO₃⁻-N per hectare and harvested plants treated with 40 kilograms NO₃⁻-N per hectare remained low for the duration of the experiment. Acetylene reduction of unharvested alfalfa treated with 40 kilograms N per hectare declined to an intermediate level and appeared to recover slightly by day 15. Changes in N₂-fixing capacity were accompanied by similar changes in levels of nodule soluble protein.     

Mechanism of nitrite reduction to nitrous oxide in a photodenitrifier,Rhodopseudomonas sphaeroide forma sp. denitrificans

The mechanism of anaerobic reduction of NO₂^? to N₂O in a photodenitrifier, Rhodopseudomonas sphaeroides forma sp. denitrificans, was investigated. With ascorbate-reduced phenazine methosulfate (PMS) as the electron donor, the nitrite reductase of this photodenitrifier reduced NO₂^? to NO and a trace amount of N₂O. With dithionite-reduced benzyl viologen as the electron donor, the major product of NO₂^? reduction was NH₂OH, and a trace amount of N₂O was also produced. The nitrate reductase itself had no NO reductase activity with ascorbate-reduced PMS. It was concluded that the essential product of NO₂^? reduction by the purified nitrite reductase is NO. Chromatophore membranes stoichiometrically produced N₂O from NO₂^? with any electron donor, such as dithionite-redduced benzyl viologen, ascorbate-reduced PMS or NADH/FMN. The membranes also contrained activity of NO reduction of N₂O with either ascorbate-reduced PMS or duroquinol. The NO reductase activity with duroquinol was inhibited by antimycin A. Stoichiometric production of N₂O from N₂^? also was observed in the reconstituted NO₂^? reduction system which contained the cytochrome bc₁ complex, cytochrome c₂, the nitrite reductase and duroquinol as the electron donor. The preparation of the cytochrome bc₁ complex itself contianed NO reductase activity. From these results the mechanism of NO₂^? reduction to N₂O in this photodenitrifier was determined as the nitrite reductase reducing NO₂^? to NO with electrons from the cytochrome bc₁ complex, and NO subsequently being reduced, without release, to N₂O with electrons from the cytochrome bc₁ complex by the NO reductase, which is closely associated with the complex.     

Capacity for Denitrification and Reduction of Nitrate to Ammonia in a Coastal Marine Sediment

The capacity for dissimilatory reduction of NO₃⁻ to N₂ (N₂O) and NH₄⁺ was measured in ¹⁵NO₃⁻-amended marine sediment. Incubation with acetylene (7 × 10⁻³ atmospheres [normal]) caused accumulation of N₂O in the sediment. The rate of N₂O production equaled the rate of N₂ production in samples without acetylene. Complete inhibition of the reduction of N₂O to N₂ suggests that the “acetylene blockage technique” is applicable to assays for denitrification in marine sediments. The capacity for reduction of NO₃⁻ by denitrification decreased rapidly with depth in the sediment, whereas the capacity for reduction of NO₃⁻ to NH₄⁺ was significant also in deeper layers. The data suggested that the latter process may be equally as significant as denitrification in the turnover of NO₃⁻ in marine sediments.     

Bacterium-Based NO2− Biosensor for Environmental Applications

A sensitive NO₂⁻ biosensor that is based on bacterial reduction of NO₂⁻ to N₂O and subsequent detection of the N₂O by a built-in electrochemical N₂O sensor was developed. Four different denitrifying organisms lacking NO₃⁻ reductase activity were assessed for use in the biosensor. The relevant physiological aspects examined included denitrifying characteristics, growth rate, NO₂⁻ tolerance, and temperature and salinity effects on the growth rate. Two organisms were successfully used in the biosensor. The preferred organism was Stenotrophomonas nitritireducens, which is an organism with a denitrifying pathway deficient in both NO₃⁻ and N₂O reductases. Alternatively Alcaligenes faecalis could be used when acetylene was added to inhibit its N₂O reductase. The macroscale biosensors constructed exhibited a linear NO₂⁻ response at concentrations up to 1 to 2 mM. The detection limit was around 1 μM NO₂⁻, and the 90% response time was 0.5 to 3 min. The sensor signal was specific for NO₂⁻, and interference was observed only with NH₂OH, NO, N₂O, and H₂S. The sensor signal was affected by changes in temperature and salinity, and calibration had to be performed in a system with a temperature and an ionic strength comparable to those of the medium analyzed. A broad range of water bodies could be analyzed with the biosensor, including freshwater systems, marine systems, and oxic-anoxic wastewaters. The NO₂⁻ biosensor was successfully used for long-term online monitoring in wastewater. Microscale versions of the NO₂⁻ biosensor were constructed and used to measure NO₂⁻ profiles in marine sediment.     

Dissimilatory nitrate uptake in Paracoccus denitrificans via a Δ\̃gmH+-dependent system and a nitrate-nitrite antiport system

Respiration-driven proton translocation has been studied with the oxidant pulse method for cells of denitrifying Paracoccus denitrificans oxidizing H₂ during reduction of O₂, NO^?₃, NO^?₂ or N₂O. A simplified scheme of anaerobic electron transport and associated proton translocation is shown that is consistent with the measured $\text{H}{}^{\mathrm{+}}\text{oxidant ratios}$. Furthermore, the kinetics and energetics of NO^?₃ uptake in whole cells of P. denitrificans were studied. For this purpose, we measured H₂ consumption or N₂O production after addition of NO^?₃ to a cell suspension, which indirectly gave information about uptake (and reduction) of NO^?₃. It was found that a lag phase in H₂ consumption or N₂O production appeared whenever the membrane potential was dissipated by addition of thiocyanate, carbonyl cyanide m-chlorophenylhydrazone or triphenyl-methylphosphonium bromide. However, these lag phases were not observed when NO^?₂ was present at the moment of introduction of NO^?₃. On the basis of these findings we conclude that there are two uptake systems for NO^?₃. One system is dependent on the proton-motive force and is probably used for initiation of NO^?₃ uptake. The other is an $\text{NO}{}^{\mathrm{?}}{}_3\text{NO}{}^{\mathrm{?}}{}_2$ antiport and its function is to take over NO^?₃ uptake from the first system.     

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⁺.     

Relationship between Ureide N and N(2) Fixation, Aboveground N Accumulation, Acetylene Reduction, and Nodule Mass in Greenhouse and Field Studies with Glycine max L. (Merr)

The relationship between ureide N and N₂ fixation was evaluated in greenhouse-grown soybean (Glycine max L. Merr.) and lima bean (Phaseolus lunatus L.) and in field studies with soybean. In the greenhouse, plant N accumulation from N₂ fixation in soybean and lima bean correlated with ureide N. In soybean, N₂ fixation, ureide N, acetylene reduction, and nodule mass were correlated when N₂ fixation was inhibited by applying KNO₃ solutions to the plants. The ureide-N concentrations of different plant tissues and of total plant ureide N varied according to the effectiveness of the strain of Bradyrhizobium japonicum used to inoculate plants. The ureide-N concentrations in the different plant tissues correlated with N₂ fixation. Ureide N determinations in field studies with soybean correlated with N₂ fixation, aboveground N accumulation, nodule weight, and acetylene reduction. N₂ fixation was estimated by ¹⁵N isotope dilution with nine and ten soybean genotypes in 1979 and 1980, respectively, at the V9, R2, and R5 growth stages. In 1981, we investigated the relationship between ureide N, aboveground N accumulation, acetylene reduction, and nodule mass using four soybean genotypes harvested at the V4, V6, R2, R4, R5, and R6 growth stages. Ureide N concentrations of young stem tissues or plants or aboveground ureide N content of the four soybean genotypes varied throughout growth correlating with acetylene reduction, nodule mass, and aboveground N accumulation. The ureide-N concentrations of young stem tissues or plants or aboveground ureide-N content in three soybean genotypes varied across inoculation treatments of 14 and 13 strains of Bradyrhizobium japonicum in 1981 and 1982, respectively, and correlated with nodule mass and acetylene reduction. In the greenhouse, results correlating nodule mass with N₂ fixation and ureide N across strains were variable. Acetylene reduction in soybean across host-strain combinations did not correlate with N₂ fixation and ureide N. N₂ fixation, ureide N, acetylene reduction, and nodule mass correlated across inoculation treatments with strains of Bradyrhizobium spp. varying in effectiveness on lima beans. Our data indicate that ureide-N determinations may be used as an additional method to acetylene reduction in studies of the physiology of N₂ fixation in soybean. Ureide-N measurements also may be useful to rank strains of B. japonicum for effectiveness of N₂ fixation.     

Denitrification in soil amended with thermophile-fermented compost suppresses nitrate accumulation in plants

NO ₃ ^? is a major nitrogen source for plant nutrition, and plant cells store NO ₃ ^? in their vacuoles. Here, we report that a unique compost made from marine animal resources by thermophiles represses NO ₃ ^? accumulation in plants. A decrease in the leaf NO ₃ ^? content occurred in parallel with a decrease in the soil NO ₃ ^? level, and the degree of the soil NO ₃ ^? decrease was proportional to the compost concentration in the soil. The compost-induced reduction of the soil NO ₃ ^? level was blocked by incubation with chloramphenicol, indicating that the soil NO ₃ ^? was reduced by chloramphenicol-sensitive microbes. The compost-induced denitrification activity was assessed by the acetylene block method. To eliminate denitrification by the soil bacterial habitants, soil was sterilized with γ irradiation and then compost was amended. After the 24-h incubation, the N₂O level in the compost soil with presence of acetylene was approximately fourfold higher than that in the compost soil with absence of acetylene. These results indicate that the low NO ₃ ^? levels that are often found in the leaves of organic vegetables can be explained by compost-mediated denitrification in the soil.     

Denitrification and nitrous oxide effluxes in boreal, eutrophic river sediments under increasing nitrate load: a laboratory microcosm study

Intact sediment cores from rivers of the Bothnian Bay (Baltic Sea) were studied for denitrification based on benthic fluxes of molecular nitrogen (N₂) and nitrous oxide (N₂O) in a temperature controlled continuous water flow laboratory microcosm under 10, 30, 100, and 300 μM of ¹⁵N enriched nitrate (NO₃ ^?, ~98 at. %). Effluxes of both N₂ and N₂O from sediment to the overlying water increased with increasing NO₃ ^? load. Although the ratio of N₂O to N₂ increased with increasing NO₃ ^? load, it remained below 0.04, N₂ always being the main product. At the NO₃ ^? concentrations most frequently found in the studied river water (10–100 μM), up to 8% of the NO₃ ^? was removed in denitrification, whereas with the highest concentration (300 μM), the removal by denitrification was less than 2%. However, overall up to 42% of the NO₃ ^? was removed by mechanisms other than denitrification. As the microbial activity was simultaneously enhanced by the NO₃ ^? load, shown as increased oxygen consumption and dissolved inorganic carbom efflux, it is likely that a majority of the NO₃ ^? was assimilated by microbes during their growth. The ¹⁵N content in ammonium (NH₄ ⁺) in the efflux was low, suggesting that reduction of NO₃ ^? to NH₄ ⁺ was not the reason for the NO₃ ^? removal. This study provides the first published information on denitrification and N₂O fluxes and their regulation by NO₃ ^? load in eutrophic high latitude rivers.     

Greenhouse Gas Emissions, Nitrate Leaching, and Biomass Yields from Production of Miscanthus × giganteus in Illinois, USA

Understanding the effects of nitrogen (N) fertilization on Miscanthus × giganteus greenhouse gas emissions, nitrate leaching, and biomass production is an important consideration when using this grass as a biomass feedstock. The objective of this study was to determine the effect of three N fertilization rates (0, 60, and 120?kg?N?ha^?1 using urea as the N source) on nitrous oxide (N₂O) and carbon dioxide (CO₂) emissions, nitrogen leaching, and the biomass yields and N content of M. × giganteus planted in July 2008, and evaluated from 2009 through early 2011 in Urbana, Illinois, USA. While there was no biomass yield response to N fertilization rates in 2009 and 2010, the amount of N in the harvested biomass in 2010 was significantly greater at the 60 and 120?kg?N?ha^?1?N rates. There was no significant CO₂ emission response to N rates in 2009 or 2010. Similarly, N fertilization did not increase cumulative N₂O emissions in 2009, but cumulative N₂O emissions did increase in 2010 with N fertilization. During 2009, nitrate (NO ₃ ^? ) leaching at the 50-cm soil depth was not related to fertilization rate, but there was a significant increase in NO ₃ ^? leaching between the 0 and 120?kg?N?ha^?1 treatments in 2010 (8.9 and 28.9?kg?NO₃?CN?ha^?1?year^?1, respectively). Overall, N fertilization of M. × giganteus led to N₂O releases, increased fluxes of inorganic N (primarily NO ₃ ^? ) through the soil profile; and increased harvested N without a significant increase in biomass production.     

Factors affecting the reduction of acetylene by Rhizobium-soybean cell associations in vitro

The acetylene reduction assay was used to measure presumed N₂-reducing activity in Rhizobium-soybean cell associations in vitro. No acetylene reduction was observed in liquid suspensions of these organisms, but cells plated onto an agar medium from a liquid suspension of Rhizobium and soybean cells exhibited acetylene-dependent production of ethylene after 7 to 14 days. Aggregates of soybean cells 0.5 to 2.0 mm in diameter were required for this activity. Decreasing oxygen from 0.20 atm to 0.10, 0.04, or 0.00 atm completely inhibited acetylene reduction. The presence of 2,4-dichlorophenoxyacetic acid or kinetin increased endogenous ethylene production and inhibited acetylene-dependent ethylene production. Acetylene reduction was observed with three out of four strains of R. japonicum tested, and three rhizobial strains, which produce root nodules on cowpeas but not soybeans, formed an association capable of acetylene-dependent ethylene production.     

Effects of Litter Inputs on N<Subscript>2</Subscript>O Emissions from a Tropical Rainforest in Southwest China

Litter inputs are expected to have a strong impact on soil N₂O efflux. This study aimed to assess the effects of the litter decomposition process and nutrient efflux from litter to soil on soil N₂O efflux in a tropical rainforest. A paired study with a control (L) treatment and a litter-removed (NL) treatment was followed for 2 years, continuously monitoring the effects of these treatments on soil N₂O efflux, fresh litter input, decomposed litter carbon (LCI) and nitrogen (LNI), soil nitrate (NO₃ ^?–N), ammonium (NH₄ ⁺–N), dissolved organic carbon (DOC), and dissolved nitrogen (DN). Soil N₂O flux was 0.48 and 0.32 kg N₂O–N ha^?1 year^?1 for the L and NL treatments, respectively. Removing the litter caused a decrease in the annual soil N₂O emission by 33%. The flux values from the litter layer were higher in the rainy season as compared to the dry season (2.10 ± 0.28 vs. 1.44 ± 0.35 μg N m^?2 h^?1). The N₂O fluxes were significantly correlated with the soil NO₃ ^?–N contents (P < 0.05), indicating that the N₂O emission was derived mainly from denitrification as well as other NO₃ ^? reduction processes. Suitable soil temperature and moisture sustained by rainfall were jointly attributed to the higher soil N₂O fluxes of both treatments in the rainy season. The N₂O fluxes from the L were mainly regulated by LCI, whereas those from the NL were dominated jointly by soil NO₃ ^? content and temperature. The effects of LCI and LNI on the soil N₂O fluxes were the greatest in the 2 months after litter decomposition. Our results show that litter may affect not only the variability in the quantity of N₂O emitted, but also the mechanisms that govern N₂O production. However, further studies are still required to elucidate the impacting mechanisms of litter decomposition on N₂O emission from tropical forests.     

N2O and CH4 Emissions,and NO3 − Leaching on a Crop-Yield Basis from a Subtropical Rain-fed Wheat–Maize Rotation in Response to Different Types of Nitrogen Fertilizer

Guaranteeing high crop yields while reducing environmental impacts of nitrogen fertilizer use due to associated losses of N₂O emissions and nitrate (NO₃ ^?) leaching is a key challenge in the context of sustainable intensification of crop production. However, few field data sets are available that explore the effect of different forms of N management on yields as well as on N losses in the form of N₂O or NO₃ ^?. Here we report on a large-scale field lysimeter (8 × 4 m²) experiment, which was designed to determine soil CH₄ and N₂O emissions, NO₃ ^? leaching losses and crop yields from a subtropical rain-fed wheat–maize rotation in the Sichuan Basin, one of the most intensively used agricultural regions in China. One control and three different fertilizer treatments with the same total rate of N application (280 kg N ha^?1 y^?1) were included: NF: control (no fertilizer); NPK: synthetic N fertilizer; OMNPK: synthetic N fertilizer plus pig manure; RSDNPK: synthetic N fertilizer plus crop residues. As compared to the standard NPK treatment, annual NO₃ ^? leaching losses for OMNPK and RSDNPK treatments were decreased by 36 and 22%, respectively (P < 0.05). Similarly, crop yield-scaled NO₃ ^? leaching for NPK treatment was higher than those for either OMNPK or RSDNPK treatments (P < 0.05). Direct N₂O emissions for RSDNPK treatment were decreased as compared with NPK and OMNPK treatments (P < 0.05). Furthermore, the yield-scaled GWP (global warming potential) was lower for the treatments where either pig manure or crop residues were incorporated as compared to the standard NPK treatment (P < 0.05). Our study indicates that it is possible to reduce the negative environmental impact of NO₃ ^? leaching and N₂O emissions without compromising crop productivity. Yield-scaled NO₃ ^? leaching, similar to the yield-scaled GWP, represents another valuable-integrated metric to address the dual goals of reducing nitrogen pollution and maintaining crop grain yield for a given agricultural system.     

Mechanism leading to N<Subscript>2</Subscript>O production in wastewater treating biofilm systems

Wastewater treatment plants are known to be important point sources for nitrous oxide (N₂O) in the anthropogenic N cycle. Biofilm based treatment systems have gained increasing popularity in the treatment of wastewater, but the mechanisms and controls of N₂O formation are not fully understood. Here, we review functional groups of microorganism involved in nitrogen (N) transformations during wastewater treatment, with emphasis on potential mechanism of N₂O production in biofilms. Biofilms used in wastewater treatment typically harbour aerobic and anaerobic zones, mediating close interactions between different groups of N transforming organisms. Current models of mass transfer and biomass interactions in biofilms are discussed to illustrate the complex regulation of N₂O production. Ammonia oxidizing bacteria (AOB) are the prime source for N₂O in aerobic zones, while heterotrophic denitrifiers dominate N₂O production in anoxic zones. Nitrosative stress ensuing from accumulation of NO₂ ^? during partial nitrification or denitrification seems to be one of the most critical factors for enhanced N₂O formation. In AOB, N₂O production is coupled to nitrifier denitrification triggered by nitrosative stress, low O₂ tension or low pH. Chemical N₂O production from AOB intermediates (NH₂OH, HNO, NO) released during high NH₃ turnover seems to be limited to surface-near AOB clusters, since diffusive mass transport resistance for O₂ slows down NH₃ oxidation rates in deeper biofilm layers. The proportion of N₂O among gaseous intermediates (NO, N₂O, N₂) in heterotrophic denitrification increases when NO or nitrous acid (HNO₂) accumulates because of increasing NO₂ ^?, or when transient oxygen intrusion impairs complete denitrification. Limited electron donor availability due to mass transport limitation of organic substrates into anoxic biofilm zones is another important factor supporting high N₂O/N₂ ratios in heterotrophic denitrifiers. Biofilms accommodating Anammox bacteria release less N₂O, because Anammox bacteria have no known N₂O producing metabolism and reduce NO₂ ^? to N₂, thereby lowering nitrosative stress to AOB and heterotrophs.     

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.     

Nitrous Oxide Production by Organisms Other than Nitrifiers or Denitrifiers

Heterotrophic bacteria, yeasts, fungi, plants, and animal breath were investigated as possible sources of N₂O. Microbes found to produce N₂O from NO₃⁻ but not consume it were: (i) all of the nitrate-respiring bacteria examined, including strains of Escherichia, Serratia, Klebsiella, Enterobacter, Erwinia, and Bacillus; (ii) one of the assimilatory nitrate-reducing bacteria examined, Azotobacter vinelandii, but not Azotobacter macrocytogenes or Acinetobacter sp.; and (iii) some but not all of the assimilatory nitrate-reducing yeasts and fungi, including strains of Hansenula, Rhodotorula, Aspergillus, Alternaria, and Fusarium. The NO₃⁻-reducing obligate anaerobe Clostridium KDHS2 did not produce N₂O. Production of N₂O occurred only in stationary phase. The nitrate-respiring bacteria produced much more N₂O than the other organisms, with yields of N₂O ranging from 3 to 36% of 3.5 mM NO₃⁻. Production of N₂O was apparently not regulated by ammonium and was not restricted to aerobic or anaerobic conditions. Plants do not appear to produce N₂O, although N₂O was found to arise from some damaged plant tops, probably due to microbial growth. Concentrations of N₂O above the ambient level in the atmosphere were found in human breath and appeared to increase after a meal of high-nitrate food.     

Growth, denitrification and nitrate ammonification of the rhizobial strain TNAU 14 in presence and absence of C2H4 and C2H2

Soil-N (NO₃ ^?) initiates as far as a threshold concentration is surpassed manifold physiological reactions on N₂-fixation. Organic N and ammonium oxidised to NO₃ ^? means oxygen depletion. Plants suffering under O₂ or infection stress start to excrete ethylene (C₂H₄). C₂H₄ widens the root intercellulars that O₂-respiration will continue. Now microbes may more easily enter the plant interior by transforming the reached methionine into C₂H₄. Surplus nitrate and C₂H₄ inhibit nodulation of leguminous plants. Excess NO₃ ^? in the nodulesphere could be diminished by N₂-fixing bacteria which in addition can denitrify or ammonify nitrate. Consequently, it was asked whether C₂H₄ interferes with the potential of N₂-fixing bacteria to reduce nitrate. The groundnut-nodule isolate TNAU 14, from which it was known that it denitrifies and ammonifies nitrate, served as inoculum of a KNO₃-mannitol-medium that was incubated under N₂-, 1% (v/v) N₂?C₂H₄-, and 1% (v/v) N₂?C₂H₂-atmosphere in the laboratory. C₂H₂ was included into the experiments because it is frequently used to quantify N₂-fixing potentials (acetylene reduction array, ARA). Gene-16S rDNA-sequencing and physiological tests revealed a high affiliation of strain TNAU 14 toRhizobium radiobacter andRhizobium tumefaciens. Strain TNAU 14 released N₂O into the bottle headspace in all treatments, surprisingly significantly less in presence of C₂H₂. Nitrate-ammonification was even completely blocked by C₂H₂. C₂H₄, in contrast rather stimulated growth, denitrification, and nitrate-ammonification of strain TNAU 14 which consumed the released NH₄ ⁺ during continuing incubation.     

An in-depth look into a tropical lowland forest soil: nitrogen-addition effects on the contents of N2O, CO2 and CH4 and N2O isotopic signatures down to 2-m depth

Atmospheric nitrogen (N) deposition is rapidly increasing in tropical regions. We investigated how a decade of experimental N addition (125 kg N ha^?1 year^?1) to a seasonal lowland forest affected depth distribution and contents of soil nitrous oxide (N₂O), carbon dioxide (CO₂) and methane (CH₄), as well as natural abundance isotopic signatures of N₂O, nitrate (NO₃ ^?) and ammonium (NH₄ ⁺). In the control plots during dry season, we deduced limited N₂O production by denitrification in the topsoil (0.05–0.40 m) as indicated by: ambient N₂O concentrations and ambient ¹⁵N-N₂O signatures, low water-filled pore space (35–60%), and similar ¹⁵N signatures of N₂O and NO₃ ^?. In the subsoil (0.40–2.00 m), we detected evidence of N₂O reduction to N₂ during upward diffusion, indicating denitrification activity. During wet season, we found that N₂O at 0.05–2.00 m was mainly produced by denitrification with substantial further reduction to N₂, as indicated by: lighter ¹⁵N-N₂O than ¹⁵N-NO₃ ^? throughout the profile, and increasing N₂O concentrations with simultaneously decreasing ¹⁵N-N₂O enrichment with depth. These interpretations were supported by an isotopomer map and by a positive correlation between ¹⁸O-N₂O and ¹⁵N-N₂O site preferences. Long-term N addition did not affect dry-season soil N₂O-N contents, doubled wet-season soil N₂O-N contents, did not affect ¹⁵N signatures of NO₃ ^?, and reduced wet-season ¹⁵N signatures of N₂O compared to the control plots. These suggest that the increased NO₃ ^? concentrations have stimulated N₂O production and decreased N₂O-to-N₂ reduction. Soil CO₂-C contents did not differ between treatments, implying that N addition essentially did not influence soil C cycling. The pronounced seasonality in soil respiration was largely attributable to enhanced topsoil respiration as indicated by a wet-season increase in the topsoil CO₂-C contents. The N-addition plots showed reduced dry-season soil CH₄-C contents and threshold CH₄ concentrations were reached at a shallower depth compared to the control plots, revealing an N-induced stimulation of methanotrophic activity. However, the net soil CH₄ uptake rates remained similar between treatments possibly because diffusive CH₄ supply from the atmosphere largely limited CH₄ oxidation.