Gerboles Michel, Lagler Fritz, Rembges Diana, Brun Claude
Institute for Environment and Sustainability, Joint Research Centre, I-21020 Ispra, VA.
J Environ Monit. 2003 Aug;5(4):529-40. doi: 10.1039/b302358c.
Hereafter, an assessment of the ability of the chemiluminescence method to measure ambient NO2 with an accuracy within 15%, as requested by the data quality objective of European directive 1999/30/CE, is presented. In general, uncertainty is evaluated using the response to reference materials or by means of inter-comparisons used to determine some statistics like repeatability, reproducibility and calibration bias. These are incomplete approaches and the method of the Guide to the Expression of Uncertainty in Measurement, advised by the Directive, should be preferred. In fact, even if it requires a large data set, it allows the relative influence of all possible sources of uncertainty to be studied. The extent of NO2 uncertainty is mainly dependent on the level of NO. It is decreased by NOx and the correlation between NOx and NO. Furthermore, the uncertainty budget reveals that the contribution of accuracy of calibration standard, linearity, converter efficiency and drift of the analyser between calibration checks to the overall uncertainty is less important than the contribution of interference, mainly humidity and PAN in rural areas. The relative expanded uncertainty of the NO2 hourly average exceeds 30% for NO2 concentrations lower than 40 microg m(-3). Nevertheless, the data quality objective of 15% is reached for 200 microg m(-3), the hourly limit value of the European directive. On the contrary, at the limit value on the annual average, 40 microg m(-3), the data quality objective is not met if NO is higher than 100 microg m(-3). However, the data quality objective could be reached by correcting the measurements with the bias due to interference.
在此,按照欧洲指令1999/30/CE的数据质量目标要求,对化学发光法测量环境二氧化氮的能力进行了评估,其测量精度在15%以内。一般来说,不确定度是通过对参考物质的响应或通过用于确定诸如重复性、再现性和校准偏差等统计数据的比对来评估的。这些方法并不完善,应优先采用该指令所建议的《测量不确定度表示指南》中的方法。事实上,即使它需要大量数据集,但它能研究所有可能不确定度来源的相对影响。二氧化氮不确定度的程度主要取决于一氧化氮的水平。它会因氮氧化物以及氮氧化物与一氧化氮之间的相关性而降低。此外,不确定度预算表明,在校准检查之间,校准标准的准确性、线性度、转换器效率和分析仪的漂移对总体不确定度的贡献,不如干扰因素(主要是农村地区的湿度和过氧乙酰硝酸酯)的贡献重要。对于低于40微克/立方米的二氧化氮浓度,二氧化氮每小时平均值的相对扩展不确定度超过30%。然而,对于欧洲指令的每小时限值200微克/立方米,达到了15%的数据质量目标。相反,在年平均值的限值40微克/立方米时,如果一氧化氮高于100微克/立方米,则无法达到数据质量目标。不过,通过校正因干扰产生的偏差来进行测量,数据质量目标是可以实现的。