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

机译:农业土壤中生物硝酸盐和挥发性有机化合物对硝化速率的影响

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摘要

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 (KNO3) in terms of redox metabolism potential. Repeated NH4–N addition increased nitrification rates (mM NO31- 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 KNO3 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: NO31- reduction 4.01 ± 0.22, Fe3+ reduction 5.37 ± 0.12, SO42- reduction 9.56 ± 0.16, and CH4 production (μg g-1 soil) 0.46 ± 0.05. Biogenic nitrate inhibited denitrificaton 1.4 times more strongly compared to mineral KNO3. Raman spectra indicated that aliphatic hydrocarbons increased in soil during nitrification, and these compounds probably bind to NO3 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.
机译:尚未完全了解调节土壤中硝化作用的过程。在这里,我们提供的证据表明,硝化过程中产生的复合硝酸盐分子和微生物挥发性有机化合物(mVOC)可能会影响土壤中的硝化速率。进行实验以阐明硝化器产生的mVOC和生物硝酸盐的整体性质,以及它们对硝化和氧化还原代谢的影响。将土壤在三种生物硝酸盐水平下孵育。就氧化还原代谢潜力而言,将含有生物硝酸盐的土壤与含有无机硝酸盐(KNO3)的土壤进行了比较。重复添加NH4–N使硝化速率(mM NO3 1-产生的g -1 土壤d -1 )从0.49增加到0.65。硝化速率较高的土壤中,16S rRNA基因的丰度提高(p <0.01)约8倍,硝化细菌的amoA基因的丰度提高约25倍,硝化古细菌的amoA基因的丰度提高约15倍。将具有生物硝酸盐和KNO3的土壤在缺氧条件下孵育以进行厌氧呼吸。含生物硝酸盐的土壤中不同氧化还原代谢的最高速率(mM电子受体降低g -1 土壤d -1 )为:NO3 1-减少4.01±0.22,Fe 3 + 减少5.37±0.12,SO4 2-减少9.56±0.16和CH4产生(μgg -1 土壤)0.46±0.05。与矿物质硝酸钾相比,生物硝酸盐对反硝化作用的抑制作用强1.4倍。拉曼光谱表明,硝化过程中土壤中的脂肪烃增加,这些化合物可能与NO3结合形成生物硝酸盐。硝化器产生的mVOC可提高(p <0.05)硝化速率和硝化细菌的丰度。实验表明,生物硝酸盐和mVOC会影响土壤中的硝化作用和氧化还原代谢。

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