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The quantification of NOsubix/i/sub and SOsub2/sub point source emission flux errors of mobile differential optical absorption spectroscopy on the basis of the Gaussian dispersion model: a simulation study

机译:在高斯分散模型的基础上,在高斯分散模型的基础上,否 x 和SO 2 点源发射通量误差:a仿真研究

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Mobile differential optical absorption spectroscopy (mobile DOAS) has become an important tool for the quantification of emission sources, including point sources (e.g., individual power plants) and area emitters (e.g., entire cities). In this study, we focused on the error budget of mobile DOAS measurements from point sources, and we also offered recommendations for the optimum settings of such measurements via a simulation with a modified Gaussian plume model. Following the analysis, we conclude that (1)?the proper sampling resolution should be between 5 and 50 m. (2)?When measuring far from the source, undetectable flux (measured slant column densities (SCDs) are under the detection limit) resulting from wind dispersion is the main error source. The threshold for the undetectable flux can be lowered by larger integration time. When measuring close to the source, low sampling frequency results in large errors, and wind field uncertainty becomes the main error source of SO2 flux (for NOx this error also increases, but other error sources dominate). More measurement times can lower the flux error that results from wind field uncertainty. The proper wind speed for mobile DOAS measurements is between 1 and 4 m s?1. (3)?The remaining errors by [NOx] ∕ [NO2] ratio correction can be significant when measuring very close. To minimize the [NOx] ∕ [NO2] ratio correction error, we recommend minimum distances from the source, at which 5 % of the NO2 maximum reaction rate is reached and thus NOx steady state can be assumed. (4)?Our study suggests that emission rates  30 g s?1 for NOx and  50 g s?1 for SO2 are not recommended for mobile DOAS measurements. Based on the model simulations, our study indicates that mobile DOAS measurements are a very well-suited tool to quantify point source emissions. The results of our sensitivity studies are important to make optimum use of such measurements.
机译:移动差分光学吸收光谱(移动DOA)已成为用于量化发射源的重要工具,包括点源(例如,各个发电厂)和区域发射器(例如,整个城市)。在这项研究中,我们专注于移动DOA测量的错误预算从点来源,我们还通过用修改的高斯羽模型模拟提供了这种测量的最佳设置的建议。在分析后,我们得出结论(1)?适当的采样分辨率应在5到50米之间。 (2)?在远离源测量时,未检测到的通量(测量的倾斜柱密度(SCDS)由风分散导致的检测极限是主要误差源。可以通过较大的集成时间降低未检测到的磁通量的阈值。当测量靠近源时,低采样频率导致大错误,风场不确定性变为SO2通量的主要误差源(对于NOx,此错误也增加,但其他错误源主导地位)。更多的测量时间可以降低风场不确定性导致的磁通误差。移动DOA测量的适当风速在1到4米之间?1之间。 (3)?在测量非常接近时,[NOx] / [NO2]比率校正的剩余误差可能是显着的。为了最小化[NOx] / [No2]比率校正误差,我们建议距离源的最小距离,此处达到5%的NO2最大反应速率,因此可以假设NOx稳定状态。 (4)?我们的研究表明,对于Moby DoAS测量,不建议为NOx和<50g S?1进行NOx和<50g S?1的排放率<50g s?1。根据模型仿真,我们的研究表明,移动DOA测量是一种非常适合量化点源排放的工具。我们的敏感性研究的结果对于实现此类测量的最佳使用非常重要。

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