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Nitrification Rates Are Affected by Biogenic Nitrate and Volatile Organic Compounds in Agricultural Soils

The processes regulating nitrification in soils are not entirely understood. Here we provide evidence that nitrification rates in soil may be affected by complexed nitrate molecules and microbial volatile organic compounds (mVOCs) produced during nitrification. Experiments were carried out to elucid...

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Detalles Bibliográficos
Autores principales: Mohanty, Santosh Ranjan, Nagarjuna, Mounish, Parmar, Rakesh, Ahirwar, Usha, Patra, Ashok, Dubey, Garima, Kollah, Bharati
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Frontiers Media S.A. 2019
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6527594/
https://www.ncbi.nlm.nih.gov/pubmed/31139154
http://dx.doi.org/10.3389/fmicb.2019.00772
Descripción
Sumario:The processes regulating nitrification in soils are not entirely understood. Here we provide evidence that nitrification rates in soil may be affected by complexed nitrate molecules and microbial volatile organic compounds (mVOCs) produced during nitrification. Experiments were carried out to elucidate the overall nature of mVOCs and biogenic nitrates produced by nitrifiers, and their effects on nitrification and redox metabolism. Soils were incubated at three levels of biogenic nitrate. Soils containing biogenic nitrate were compared with soils containing inorganic fertilizer nitrate (KNO(3)) in terms of redox metabolism potential. Repeated NH(4)–N addition increased nitrification rates (mM NO(3)(1-) produced g(-1) soil d(-1)) from 0.49 to 0.65. Soils with higher nitrification rates stimulated (p < 0.01) abundances of 16S rRNA genes by about eight times, amoA genes of nitrifying bacteria by about 25 times, and amoA genes of nitrifying archaea by about 15 times. Soils with biogenic nitrate and KNO(3) were incubated under anoxic conditions to undergo anaerobic respiration. The maximum rates of different redox metabolisms (mM electron acceptors reduced g(-1) soil d(-1)) in soil containing biogenic nitrate followed as: NO(3)(1-) reduction 4.01 ± 0.22, Fe(3+) reduction 5.37 ± 0.12, SO(4)(2-) reduction 9.56 ± 0.16, and CH(4) production (μg g(-1) soil) 0.46 ± 0.05. Biogenic nitrate inhibited denitrificaton 1.4 times more strongly compared to mineral KNO(3). Raman spectra indicated that aliphatic hydrocarbons increased in soil during nitrification, and these compounds probably bind to NO(3) to form biogenic nitrate. The mVOCs produced by nitrifiers enhanced (p < 0.05) nitrification rates and abundances of nitrifying bacteria. Experiments suggest that biogenic nitrate and mVOCs affect nitrification and redox metabolism in soil.