10. NITROGEN TURNOVER Nitrogen – very important component of all and esp. of microbial cells (amino acids, proteins, nucleic acids,) 10.1. Ammonification = the main mineralization reaction in Ncycling, very typical especially in soils Organic N-substances NH3, NH4+ Main substances for ammonification: amino acids, proteins, nucleic acids, urea, chitin, uric acid, peptidoglycan… Aerobic and anaerobic Psychrophils, mesophils, thermophils Ammonification is significantly influenced by C:N ratio: 25 : 1 – OK for microorganisms – they have enough energy sources and nutrients (C + N) < 25 : 1 - Surplus of nitrogen – high production of NH3 < 25 : 1 – Shortage of nitrogen in decomposable material, slow breakdown of substances, N from other sources will be used (soil solution); result = immobilization - flow of N into microbial cells The use of NH4+ - source of N for biosynthesis (microorganisms prefer often NH4+to NO3-, ± plants) - source of energy through nitrification - volatisation - sorption on soil clays and organic matter - component of soil exchange complex - leaching (underground and surface water Protein ammonification The most important ammonification Protein hydrolysis to amino acids Amino acids deamination NH3 Aerobic products - NH3, CO2…. (Bacillus, Pseudomonas…) Anaerobic products - NH3, CO2, H2S, scatol, indol, mercaptans…. (Clostridium…) 10.2. Autotrophic nitrification Aerobic oxidation of NH3 in two steps Chemolithotrophic autotrophs Source of energy for nitrifying bacteria Conditions: aeration, pH (opt. 6.6 – 8.0), moisture, temperature Nitrification = index of soil fertility Nitritation NH4+ + O2 NO2- + H2O (+E) Nitrosomonas, Nitrosococcus, Nitrosocystis Nitratation NO2- + O2 NO3- (+E) (Nitrobacter, Nitrococcus) Significance of nitrification Source of energy for nitrifying bacteria NO3- - main source of N for plants NO3- is used in denitrification NO3- is less stable in soil (anion), the result - high losses of N Leaching into underground water – limitation for its use as a drinking water Leaching into surface water – it could resulted in eutrophisation = developing of algae, the biomass decomposition using O2 Shortage of O2 for higher organisms Nitrification in farm yard manure is undesirable – it can result in nitrogen losses 10.3. Heterotrophic nitrification Heterotrophic bacteria and fungi convert organic N-substances directly to NO3- – the rate is 4times slower than autotrophic nitrification RNH2 RNHOH RNO RNO3 NO3-3 -1 +1 +3 +5 Typical for acidic environment Bacteria: Arthrobacter, Mycobacterium Fungi:Aspergillus,Penicillium, Cladosporium 10.4. Denitrification = microbial reduction of NO3- in anaerobic conditions Dissimilative denitrification NO3- NO2- NO N 2O N2 = alternative respiration chain in which O from nitrates is an acceptor of H+ - for denitrifiers the source of energy - mostly heterotrophic bacteria, strong dependence on C availability - denitrifying genera: Pseudomonas, Alcaligenes, Bacillus, Thiobacillus, Rhizobium, Paracoccus - conditions: -O2, N oxides (NO3-) as oxidant, organic substances or HS- or NH4- as reductant - agriculturally undesirable soil process – loss of nitrogen - environmentally: when the N-oxides are produced = undesirable process – changes in atmosphere (green-houses gasses) Assimilative denitrification = anaerobic respiration NO3- + H+ NH4+ + H2O (+E) - for denitrifiers the source of energy - if surplus of NO3- process positive, NH4+ more stabile in the soil - the use of NH4+ - see ammonification 10.5. N2 fixation very important process returning N2 to soil Total inputs – (kg. year-1) (Paul, Clark, 1996): N2 fixation 175 000 Fertilizers 85 000 Lightning 20 000 Anthropogenic 40 000 Total 320 000 Legumes 140 kg.ha-1.y-1 Rice Meadows Other cultivated crops Forest 30 kg.ha1.y-1 15 kg.ha-1.y-1 5 kg.ha-1.y-1 10 kg.ha-1.y-1 Nitrogenase reduce N2 in strictly anaerobic conditions N2 HN=NH H2N-NH2 2 NH3 2NH4+ High need for energy (ATP) Diazotrophs include: organotrophs, phototrophic sulphur bacteria, cyanobacteria Soil free living bacteria: Clostridium, Azotobacter Associative bacteria: Azospirillum Symbiotic bacteria: Frankia (fixation in vesicle); Rhizobium, Bradyrhizobium etc. (fixation with bacteroids) Clostridium G+ spore forming straight anaerobic bacterium Source of energy – different organic Csubstances (from simple to complex) Present also in lower pH (> 5) Fixation approx. 5 kg.ha-1.y-1 Presence: several soils Azotobacter G- non-sporulating pleiomorphic aerobic bacterium (cocci – rods) Source of energy – simple organic Csubstances Present in neutral soils, pH close to 7 Need for P, Ca, K… Fixation approx. 5 - 10 kg.ha-1.y-1 Presence: in high quality soils Symbiotic fixation Attributed to several plants Most important in legumes (700 genera with 14000 species) Frankia and group of rhizobia (Rhizobium, Bradyrhizobium ….) Rhizobium (nodule forming bacteria) G- pleiomorphic rods (straight in soil and in laboratory media, branched in root nodules = bacteroids) N2 fixation occurs only in the roots if the content of soil nitrogen is low (organic Nsubstances, NH4+, NO3-) O2 control with leghemoglobin High demand for energy: N2+6e-+12ATP+8H- = 2NH3+12ADP+12Pi NH3 (NH4+) is incorporated into organic forms (amino acids) in the associated plant cells Process is genetically coded: Nif-genes: nitrogenase Nod-genes: nodulation Process of nodulation - attachment on the root (specific lectins) - infection of root hairs - rhizobia moving through root - forming plant peribacteroid membrane (fixation is carried on by specialized cells) - rhizobia change into bacteroids - nitrogen fixation (plant is giving sugars, rhizobia NH3) = “pure symbiosis” - destroying of old nodules, lyses of cells, mineralization Level of fixation: (0) – 50 – 150 (800) kg.ha-1.y-1 Inoculation To improve N2 fixation seeds could be inoculated before sowing Rhizobia are specific for nearly each plant genera 10.6. Immobilisation Inorganic substances are used in biosynthesis to produce organic substances as a component of living cells (result = cell growing, cell division) Inorganic Organic Demand for energy Examples: NH4+ Amino acids SO42- Methionine (amino acid) H2PO4- + ADP CO2 Proteins ATP Glucose Influence of biogenic elements ratio (optimum): C:N 25 : 1 C:P 100 : 1 C:S 400 : 1 Very typical process for soil – flow of elements from soil solution into microbial cells Significance for soil Positive – when nutrients are in surplus, leaching is avoided, the nutrients are “stored” in microbial cells, their death and mineralization return nutrients into soil Negative – when there are not enough nutrients in soil, the competition appears between plants a microorganisms