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Temperature affects the kinetics of nitrite oxidation and nitrification coupling in four agricultural soils

机译:温度影响四种农业土壤中亚硝酸盐氧化和硝化耦合的动力学

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The oxidation of ammonia (NH3) to nitrite (NO2-) by archaea and bacteria (AOA and AOB) in soil has been studied intensively for > 140 y. However, relatively little attention has been focused on the activity of nitrite oxidizing bacteria (NOB), which catalyze the oxidation of NO2-, despite ample published evidence of soil NO2- accumulation, and the temperature dependent accumulation of NO2- in wastewater and aquatic environments. This study evaluated the response of NO2- oxidizing activity to temperature in four Oregon agricultural soils. Rates of NO2- oxidizing potentials (NOP) were measured at 4-42 degrees C in all soils. Evaluation of the thermodynamic parameters found that the NOB have a similar temperature range and optimal temperature as the NH3 oxidizer response observed in Taylor et al. (2016). A determination of kinetic parameters of NO2- oxidation at 17, 30, and 37 degrees C found a trend for the apparent maximum velocity (V-max) to be greater at 30 than 17 degrees C, and significant, soil-specific changes in substrate affinity (K-m ) of NO2- consumption. Although the potential rates of NO2- oxidation exceeded those of NH3 oxidation, NO2- accumulated under at least one temperature in all soils. There were only weak correlations between NO2- accumulation and rates of NH3 or NO2- oxidation, the abundance of Nitrobacter nxrA or Nitrospira nxrB genes or the total (nxrA + nxrB)/amoA gene ratio. The apparent K-m did not correlate with NO2- accumulation at any temperature; however, utilizing the obtained V-max and K-m we found that Michaelis-Menten kinetics predict that an accumulation of measurable NO2- is required to drive equal rates of NH3 and NO2- oxidation. Implications of reductions in NO2- affinity by NOB at some temperatures that result in increased NO2- accumulation in soils include plant toxicity and the loss of soil N through increased production of reactive N-oxide gases.
机译:在土壤中氧化氨(NH3)氧化到亚硝酸盐(NO 2-)的土壤中的氧化(AOA和AOB),用于> 140 y。然而,相对较少的关注旨在赋予亚硝酸盐氧化细菌(NOB)的活性,该细菌催化NO2-的氧化,尽管有充足的土壤NO2-积累证据,以及NO2-在废水和水生环境中的温度依赖性积累。该研究评估了No2-氧化活性在四个俄勒冈农业土壤中的响应。在所有土壤中在4-42℃下测量No2-氧化潜力(NOP)的速率。评估热力学参数发现,除了在Taylor等人观察到的NH3氧化剂反应时,NO的效率范围和最佳温度具有相似的温度范围和最佳温度。 (2016)。在17,30和37℃下测定NO2-氧化的动力学参数,发现表观最大速度(V-MAX)在30多℃下更大,底物的显着土壤特异性变化更大NO2消费的亲和力(KM)。尽管NO 2氧化的潜在速率超过了NH 3氧化的速率,但在所有土壤中的至少一个温度下累积了NO 2。 NH 3或NO 2-氧化的NO 2和NO 2的速率之间只有弱相关性,硝基杆菌NXRA或NITROPIRA NXRB基因或总(NXRA + NXRB)/ AMOA基因比率之间的丰富。表观K-M在任何温度下都与NO2累积不相关;然而,利用所得V-MAX和K-M发现,我们发现Michaelis-Menten动力学预测可测量的NO2的积累是为了驱动NH 3和NO2-氧化的等速率。在一些温度下,NO2-除了土壤中的NO 2增加的温度下,NOB中减少的影响包括植物毒性和通过增加反应性N-氧化物气体的生产。

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