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Kinetics of N20 production and reduction in a nitrate-contaminated aquifer inferred from laboratory incubation experiments

机译:根据实验室培养实验推断出的N20生成动力学以及硝酸盐污染的含水层的还原

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Knowledge of the kinetics of N20 production and reduction in groundwater is essential for the assessment of potential indirect emissions of the greenhouse gas. In the present study, we investigated this kinetics using a laboratory approach. The results were compared to field measurements in order to examine their transferability to the in situ conditions. The study site was the unconfined, predominantly sandy Fuhrberger Feld aquifer in northern Germany. A special characteristic of the aquifer is the occurrence of the vertically separated process zones of heterotrophic denitrification in the near-surface groundwater and of autotrophic denitrification in depths beyond 2-3 m below the groundwater table, respectively. The kinetics of N20 production and reduction in both process zones was studied during long-term anaerobic laboratory incubations of aquifer slurries using the 15N tracer technique. We measured N20, N2, NO; , NO2 , and S02 4 – concentrations as well as parameters of the aquifer material that were related to the relevant electron donors, i.e. organic carbon and pyrite. The laboratory incubations showed a low denitrification activity of heterotrophic denitrification with initial rates between 0.2 and 13pg N kg -1 d-1 . The process was carbon limited due to the poor availability of its electron donor. In the autotrophic denitrification zone, initial denitrification rates were considerably higher, ranging between 30 and 148 pg N kg-1 d-1 , and NO; as well as N20 were completely removed within 60 to 198 days. N20 accumulated during heterotrophic and autotrophic denitrification, but maximum concentrations were substantially higher during the autotrophic process. The results revealed a satisfactory transferability of the laboratory incubations to the field scale for autotrophic denitrification, whereas the heterotrophic process less reflected the field conditions due to considerably lower N20 accumulation during laboratory incubation. Finally, we applied a conventional model using first-order-kinetics to determine the reaction rate constants k1 for N20 production and k2 for N20 reduction, respectively. The goodness of fit to the experimental data was partly limited, indicating that a more sophisticated approach is essential to describe the investigated reaction kinetics satisfactorily.
机译:了解N20产生和减少地下水的动力学对于评估潜在的温室气体间接排放至关重要。在本研究中,我们使用实验室方法研究了这种动力学。将结果与现场测量结果进行比较,以检查其在现场条件下的可转移性。研究地点是德国北部无限制的主要是沙质的Fuhrberger Feld含水层。含水层的一个特殊特征是在垂直分布的近地层地下水中存在异养反硝化过程区,并且在地下水位以下2-3 m深度处发生了自养反硝化过程。在使用15N示踪剂技术对含水层进行长期厌氧实验室培养期间,研究了两个工艺区中N20产生和还原的动力学。我们测量了N20,N2,NO; ,NO2和SO2 4 –含水层材料的浓度以及与相关电子给体(即有机碳和黄铁矿)有关的参数。实验室培养表明,异养反硝化的反硝化活性低,初始速率介于0.2和13pg N kg -1 d-1之间。由于电子供体的可用性差,该过程受到碳的限制。在自养反硝化区,初始反硝化率要高得多,介于30至148 pg N kg-1 d-1和NO之间。以及N20在60至198天内被完全清除。 N20在异养和自养反硝化过程中积累,但最大浓度在自养过程中明显更高。结果表明,自培养的反硝化实验室培养物可以令人满意地转移至田间规模,而异养过程则较少反映田间条件,因为实验室培养过程中N20的累积量要低得多。最后,我们应用了使用一级动力学的常规模型来分别确定N20产生的反应速率常数k1和N20还原的反应速率常数k2。对实验数据的拟合优度在一定程度上受到限制,表明必须采用更先进的方法来令人满意地描述所研究的反应动力学。

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