首页> 外文会议>Plasma Source Mass Spectrometry, Applications and Emerging Technologies >THE USE OF A HIGH ACCURACY ISOTOPE DILUTION MASS SPECTROMETRY (IDMS) METHOD FOR THE ANALYSIS OF SULFUR IN FUEL TO SUPPORT ANALYTICAL TECHNOLOGIES USED IN INDUSTRY
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THE USE OF A HIGH ACCURACY ISOTOPE DILUTION MASS SPECTROMETRY (IDMS) METHOD FOR THE ANALYSIS OF SULFUR IN FUEL TO SUPPORT ANALYTICAL TECHNOLOGIES USED IN INDUSTRY

机译:使用高精度同位素稀释质谱法(IDMS)法用于分析燃料中的硫磺,支持工业中使用的分析技术

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A significant source of atmospheric pollution is the emission of sulfur from the combustion of fossil fuels. In addition, sulfur in fuel can reduce the efficiency of catalysts containing the platinum group elements such as those in car exhaust catalysts, leading to increased emissions of other pollutants such as NO_(2). Despite concerns about environmental impact, fossil fuels remain a significant source of energy. In 2001, the UK alone produced 106 million tonnes of crude oil from offshore sites [1]. European Community directives concerning the sulfur content of liquid fuels reflect the increasing concern about the effect of sulfur on the environment. In 1993, the legislation for sulfur content was 500 and 2000 (mu)g g~(-1) for petrol and diesel fuels respectively [2]. The current limits (set in 1998) are 150 and 350 (mu)g g~(-1) respectively and the limit for both fuels is set to be reduced to just 50 (mu)g g~(-1) by the year 2005 [3]. Similar legislation exists in other developed countries. The petroleum industry while wishing to meet legislative requirements, is also keen to avoid the additional costs of removing sulfur below the legal limit. This is a major economic reason why the industry needs high accuracy sulfur measurements. Routine techniques used in the industry for the analysis of sulfur in fuel are being put under increased pressure with the establishment of these dramatically reduced limits. This paper describes how developments in the high accuracy analysis of sulfur in fossil fuels by IDMS have lead to the support of other more routine techniques. This has been achieved by providing reference values for a round robin exercise and by the certification of reference materials. These reference materials are in the concentration range of 1 - 450 (mu)g g~(-1), which encompass all of the planned legislative limits within the EC and also any likely further reduction in these limits. Together, the reference values and reference materials provide a quality assurance of routine techniques and of their day-to-day operational performance. A European working group (WG27) was set up to evaluate which analytical techniques were best suited to meet the new European Commission levels in 1998. The working group organised a round robin exercise (1998-1999) [4] in which 85 laboratories across Europe analysed 15 petrol and diesel samples in a concentration range 50 - 500 (mu)g g~(-1). These laboratories used one of five recognised techniques for this analysis: wavelength dispersive X-ray fluorescence, energy dispersive X-ray fluorescence, Wickbold combustion, microcoulometry, and combustion/ultraviolet fluorescence. The round robin exercise was used to compare each of the methods in terms of repeatability, reproducibility and accuracy of results relative to each other. In October 2000, the working group decided to organise a second round robin exercise in order to define the precision of test methods in the concentration range 1 - 60 (mu)g g~(-1) [5]. This round robin was carried out during 2001 and consisted of 8 petrol and 8 diesel samples sent to 102 laboratories across Europe. The laboratories used one of the 5 analytical techniques as for the previous round robin study, with the exception of Wickbold combustion, which was excluded due to the poor precision of the results in round 1. Two of the round robin samples (one each of petrol and diesel) were considered "quality control" samples because they had been assigned a reference value by IDMS analysis. The IDMS results were of the highest accuracy with total expanded uncertainties (with a 95percent confidence interval) of only 2.6percent and 2.0percent for the petrol and diesel samples respectively. This was an important development for the working group since the IDMS analysis was used to provide reference values for these samples and allowed the group to define the absolute performance of the other techniques rather than just the accuracy relative to each other. Results from
机译:大气污染的重要来源是从化石燃料的燃烧中排放硫磺。此外,燃料中的硫可以降低含有铂族群元素的催化剂的效率,例如汽车排气催化剂中的催化剂,导致其他污染物的排放量增加,例如NO_(2)。尽管对环境影响有担忧,但化石燃料仍然是一个重要的能源来源。 2001年,英国单独从近海地点生产了10600万吨原油[1]。关于液体燃料硫含量的欧洲社区指令反映了对硫磺对环境的影响的越来越多。 1993年,硫含量的立法为汽油和柴油燃料的500和2000(mu)G g〜(-1)[2]。目前限制(1998年设置)为150和350(MU)GG〜(-1),燃料的极限设定为2005年的50(MU)GG〜(-1)[ 3]。在其他发达国家存在类似的立法。本石油工业在希望满足立法要求的同时,也热衷于避免额外的成本去除法定限额的硫磺。这是该行业需要高精度的硫测量的主要经济原因。在行业中使用的常规技术用于分析燃料中的硫在增加的压力下,建立这些大幅减少限制。本文介绍了IDMS通过IDMS在化石燃料中硫的高精度分析的开发如何导致其他常规技术的支持。这是通过提供循环运动的参考值和参考资料认证来实现的。这些参考资料处于1 - 450(mu)G g〜(-1)的浓度范围内,其包括EC内的所有计划的立法限额以及这些限制的可能进一步减少。在一起,参考值和参考资料提供了常规技术和日常运行性能的质量保证。欧洲工作组(WG27)被设立,评估哪些分析技术最适合于1998年满足新的欧洲委员会水平。工作组组织了一名循环运动(1998-1999)[4],其中欧洲的85个实验室分析了浓度范围50-500(mU)Gg〜(-1)的15汽油和柴油样品。这些实验室使用了该分析的五种公认技术中的一种:波长分散X射线荧光,能量分散X射线荧光,Wickbold燃烧,微型管测定法和燃烧/紫外荧光。循环练习用于将各种方法与相对于彼此相对于彼此的结果的重复性,再现性和准确性进行比较。 2000年10月,工作组决定组织第二次循环运动,以定义浓度范围1 - 60(mU)G〜(-1)[5]中试验方法的精度。这个循环罗宾于2001年进行,由8个汽油和8个柴油样本组成,送到欧洲的102个实验室。实验室使用了5个分析技术之一,如Wickbold燃烧除了Wickbold燃烧外,这是由于圆形1.圆形罗宾样本的两种循环样本(汽油中的两种)的精度较差而被排除在外和柴油)被认为是“质量控制”样本,因为它们被IDMS分析分配了参考价值。 IDMS结果具有最高的精度,其总扩展的不确定性(具有95个置信区间)仅为2.6%,分别为汽油和柴油样本。这是工作组的重要发展,因为IDMS分析用于为这些样本提供参考值,并且允许该组定义其他技术的绝对性能而不是相对于彼此的准确性。结果来自

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