DIN EN 16339-2013 Ambient air - Method for the determination of the concentration of nitrogen dioxide by diffusive sampling German version EN 16339 2013《环境空气 利用散布式取样的二氧化氮浓度测定方法 德文版.pdf

《DIN EN 16339-2013 Ambient air - Method for the determination of the concentration of nitrogen dioxide by diffusive sampling German version EN 16339 2013《环境空气 利用散布式取样的二氧化氮浓度测定方法 德文版.pdf》由会员分享，可在线阅读，更多相关《DIN EN 16339-2013 Ambient air - Method for the determination of the concentration of nitrogen dioxide by diffusive sampling German version EN 16339 2013《环境空气 利用散布式取样的二氧化氮浓度测定方法 德文版.pdf（51页珍藏版）》请在麦多课文档分享上搜索。

1、November 2013 Translation by DIN-Sprachendienst.English price group 19No part of this translation may be reproduced without prior permission ofDIN Deutsches Institut fr Normung e. V., Berlin. Beuth Verlag GmbH, 10772 Berlin, Germany,has the exclusive right of sale for German Standards (DIN-Normen).I

2、CS 13.040.20!%*,f“2070967www.din.deDDIN EN 16339Ambient air Method for the determination of the concentration of nitrogen dioxide bydiffusive sampling;English version EN 16339:2013,English translation of DIN EN 16339:2013-11Auenluft Bestimmung der Konzentration von Stickstoffdioxid mittels Passivsam

3、mler;Englische Fassung EN 16339:2013,Englische bersetzung von DIN EN 16339:2013-11Air ambiant Mthode pour la dtermination de la concentration du dioxyde dazote aumoyen dchantillonneurs par diffusion;Version anglaise EN 16339:2013,Traduction anglaise de DIN EN 16339:2013-11www.beuth.deIn case of doub

4、t, the German-language original shall be considered authoritative.Document comprises 51 pages 10.13This standard has been included in the VDI/DIN Handbook on air quality, Volume 5. DIN EN 16339:2013-11 2 A comma is used as the decimal marker. National foreword This document (EN 16339:2013) has been

5、prepared by Technical Committee CEN/TC 264 “Air quality” (Secretariat: DIN, Germany), Working Group WG 11 “Ambient air quality Diffusive samplers for the determination of gases and vapours” (Secretariat: NEN, Netherlands). The responsible German body involved in its preparation was the Kommission Re

6、inhaltung der Luft (KRdL) im VDI und DIN Normenausschuss (Commission on Air Pollution Prevention of VDI and DIN Standards Committee). National Annex NA (informative) Bibliography DIN EN 13528-1, Ambient air quality Diffusive samplers for the determination of concentrations of gases and vapours Requi

7、rements and test methods Part 1: General requirements DIN EN 13528-2, Ambient air quality Diffusive samplers for the determination of concentrations of gases and vapours Requirements and test methods Part 2: Specific requirements and test methods DIN EN 13528-3, Ambient air quality Diffusive sampler

8、s for the determination of concentrations of gases and vapours Part 3: Guide to selection, use and maintenance DIN EN 14211, Ambient air Standard method for the measurement of the concentration of nitrogen dioxide and nitrogen monoxide by chemiluminescence DIN EN ISO 16000-15, Indoor air Part 15: Sa

9、mpling strategy for nitrogen dioxide (NO2) DIN EN ISO 20988, Air quality Guidelines for estimating measurement uncertainty DIN ISO 5725 (all parts), Accuracy (trueness and precision) of measurement methods and results VDI 2453 Part 1, Gaseous air pollution measurement Determination of nitrogen dioxi

10、de concentration Photometric manual standard method (Saltzmann) VDI 3869 Part 4, Measurement of ammonia in ambient air Sampling with diffusive samplers Photometric or ion chromatographic analysis EUROPEAN STANDARD NORME EUROPENNE EUROPISCHE NORM EN 16339 July 2013 ICS 13.040.20 English Version Ambie

11、nt air - Method for the determination of the concentration of nitrogen dioxide by diffusive sampling Air ambiant - Mthode pour la dtermination de la concentration du dioxyde dazote au moyen dchantillonneurs par diffusion Auenluft - Bestimmung der Konzentration von Stickstoffdioxid mittels Passivsamm

12、ler This European Standard was approved by CEN on 15 June 2013. CEN members are bound to comply with the CEN/CENELEC Internal Regulations which stipulate the conditions for giving this European Standard the status of a national standard without any alteration. Up-to-date lists and bibliographical re

13、ferences concerning such national standards may be obtained on application to the CEN-CENELEC Management Centre or to any CEN member. This European Standard exists in three official versions (English, French, German). A version in any other language made by translation under the responsibility of a

14、CEN member into its own language and notified to the CEN-CENELEC Management Centre has the same status as the official versions. CEN members are the national standards bodies of Austria, Belgium, Bulgaria, Croatia, Cyprus, Czech Republic, Denmark, Estonia, Finland, Former Yugoslav Republic of Macedo

15、nia, France, Germany, Greece, Hungary, Iceland, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta, Netherlands, Norway, Poland, Portugal, Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland, Turkey and United Kingdom. EUROPEAN COMMITTEE FOR STANDARDIZATION COMIT EUROPEN DE NORMALISATION EUROP

16、ISCHES KOMITEE FR NORMUNG Management Centre: Avenue Marnix 17, B-1000 Brussels 2013 CEN All rights of exploitation in any form and by any means reserved worldwide for CEN national Members. Ref. No. EN 16339:2013: EEN 16339:2013 (E) 2 Contents Page Foreword 3 Introduction .4 1 Scope 5 2 Normative ref

17、erences 5 3 Terms and definitions .5 4 Principle of the method .7 5 Materials .8 6 Sampling 12 7 Analytical procedure 13 8 Calculation of the concentration of nitrogen dioxide . 16 9 Quality control/quality assurance . 17 10 Report 18 11 Performance requirements and measurement uncertainty . 18 Anne

18、x A (normative) Description of samplers 21 Annex B (informative) Other samplers . 26 Annex C (informative) Estimation of the uptake rate of the samplers 34 Annex D (informative) Measurement uncertainty . 39 Bibliography . 47 DIN EN 16339:2013-11 EN 16339:2013 (E) 3 Foreword This document (EN 16339:2

19、013) has been prepared by Technical Committee CEN/TC 264 “Air quality”, the secretariat of which is held by DIN. This European Standard shall be given the status of a national standard, either by publication of an identical text or by endorsement, at the latest by January 2014, and conflicting natio

20、nal standards shall be withdrawn at the latest by January 2014. Attention is drawn to the possibility that some of the elements of this document may be the subject of patent rights. CEN and/or CENELEC shall not be held responsible for identifying any or all such patent rights. According to the CEN/C

21、ENELEC Internal Regulations, the national standards organisations of the following countries are bound to implement this European Standard: Austria, Belgium, Bulgaria, Croatia, Cyprus, Czech Republic, Denmark, Estonia, Finland, Former Yugoslav Republic of Macedonia, France, Germany, Greece, Hungary,

22、 Iceland, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta, Netherlands, Norway, Poland, Portugal, Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland, Turkey and the United Kingdom. DIN EN 16339:2013-11 EN 16339:2013 (E) 4 Introduction Experience gained across the European Union (EU) in imp

23、lementing EU ambient air quality legislation 1 has shown that, generally, for nitrogen dioxide (NO2), meeting the annual average limit value of 40 g/m3is more problematic than meeting the 1-h limit value of 200 g/m 2. EU Directive 2008/50/EC 1 stipulates that European Union Member States shall apply

24、 the reference measurement methods and criteria specified in the Directive. For NO2monitoring in ambient air, the reference method being that described in EN 14211:2012 3. However, a Member State may use any other method that provides results equivalent to that of the reference method, to be demonst

25、rated in accordance with the Guide for the demonstration of equivalence of ambient air monitoring methods 4. The GDE devotes specific paragraphs to methods based on diffusive sampling. For the measurement of longer-term average concentrations of nitrogen dioxide for comparison with the annual averag

26、e limit value diffusive sampling is an attractive alternative to fixed monitoring using the reference methodology described in EN 14211 because of small size of diffusive samplers; no requirement for electric power; potential for covering areas with a high spatial density; cost effectiveness. Conseq

27、uently, diffusive samplers can partially substitute and supplement fixed monitoring as an instrument for the assessment of air quality, provided that they fulfil the specific Data Quality Objectives given in 1. At the time of publication of this standard, no full demonstration of equivalence accordi

28、ng to 4 has been performed. However, some studies have compared NO2annual average concentrations measured by chemiluminescence and by diffusive samplers 5, 6, 7 and 8. These have shown the potential of diffusive sampling to meet the data quality objective of 15 % expanded uncertainty for fixed measu

29、rements 1. The methodology described in this standard can be applied to obtain air quality information with a relatively high spatial density that can be used to complement the appropriate siting of fixed monitoring stations, or in the validation of dispersion models. Further, the methodology descri

30、bed can be used for simultaneously measuring sulphur dioxide (SO2) when using ion chromatography as the method of analysis. The analytical method is described in 9, 10 and 11. This standard has been prepared based on the findings of reviews of implemented diffusive samplers in the European Union 12.

31、 The methodology described in this standard may also be used to determine NO2in indoor air. Appropriate strategies for NO2measurement in indoor air are described in EN ISO 16000-15. DIN EN 16339:2013-11 EN 16339:2013 (E) 5 1 Scope This European Standard specifies a method for the sampling and analys

32、is of NO2in ambient air using diffusive sampling followed by extraction and analysis by colorimetry or ion chromatography (IC). It can be used for the NO2measurement in a concentration range of approximately 3 g/m to 130 g/m3. A sample is typically collected for a period of 1 to 4 weeks 13, with exp

33、osure periods depending on the design of the samplers and the concentration levels of NO2. Several sorbents can be used for trapping NO2in ambient air using a diffusive sampler. This standard specifies the application of triethanolamine as the reagent. Nitrous acid and peroxyacetyl nitrate are the m

34、ajor chemical interferences of sorption by triethanolamine. However, in ambient air monitoring over long sampling times, both contaminants are generally present at low concentrations relative to NO2. Moreover, these species can also interfere with the measurement of NO2when applying the EU reference

35、 method for NO2monitoring based on chemiluminescence (see 2). This standard describes the application of a tube-type sampler with either a cylindrical or a slightly conical tube. Its typical uptake rate is about 1 cm3/min. Only for this sampler type sufficient evidence of validation has been found i

36、n a literature survey 12. The relative expanded uncertainty of NO2measurements performed using these tube-type diffusive samplers can potentially be lower than 25 % for individual measurements. When aggregating results to form annual average values, the relative expanded uncertainty can be further r

37、educed to levels below 15 % due to the reduction of random effects on uncertainty 6. 2 Normative references The following documents, in whole or in part, are normatively referenced in this document and are indispensable for the application of this document. For dated references, only the edition cit

38、ed applies. For undated references, the latest edition of the referenced document (including any amendments) applies. EN ISO/IEC 17025, General requirements for the competence of testing and calibration laboratories (ISO/IEC 17025) 3 Terms and definitions For the purpose of this document, the follow

39、ing terms and definitions apply. 3.1 certified reference material reference material 3.8, characterized by a metrologically valid procedure for one or more specified properties, accompanied by a certificate that provides the value of the specified property, its associated uncertainty, and a statemen

40、t of metrological traceability SOURCE: ISO Guide 35:2006 3.2 combined standard uncertainty standard measurement uncertainty 3.10 that is obtained using the individual standard measurement uncertainties associated with the input quantities in a measurement model SOURCE: JGCM 200:2012 3.3 desorption e

41、fficiency ratio of the mass of analyte desorbed from a sampling device to that applied DIN EN 16339:2013-11 EN 16339:2013 (E) 6 SOURCE: EN 13528-2:2002 3.4 diffusive sampler device which is capable of taking samples of gases or vapours from the atmosphere at a rate controlled by a physical process s

42、uch as gaseous diffusion through a static air layer or a porous material and/or permeation through a membrane, but which does not involve the active movement of air through the device SOURCE: EN 13528-1:2002 Note 1 to entry: Active normally refers to the pumped movement of air. 3.5 diffusive uptake

43、rate rate at which the diffusive sampler collects a particular gas or vapour from the atmosphere. SOURCE: EN 13528-1:2002 Note 1 to entry: The uptake rate is usually expressed in units of (pg/(nmol/mol)/min)or (cm3/min). Note 2 to entry: pg/(nmol/mol)/minis equivalent to ng/(mol/mol)/min. 3.6 expand

44、ed (measurement) uncertainty product of a combined standard measurement uncertainty and a factor larger than the number one SOURCE: JCGM 200:2008 Note 1 to entry: The factor depends upon the type of probability distribution of the output quantity in a measurement model and on the selected coverage p

45、robability. Note 2 to entry: The term “factor” in this definition refers to a coverage factor. 3.7 field blank sealed sampler drawn from the same batch as the samplers being used for NO2monitoring. This sampler is taken unopened to the field and returned together with exposed samplers after the samp

46、ling is completed Note 1 to entry: This blank is only used for quality control purposes. Note 2 to entry: A transport blank is considered to be a special case of a field blank. A transport blank is taken to the exposure site, left unopened and returned to the laboratory immediately after placement o

47、r collection of the samplers. Transport blanks may be used when regular field blanks reveal an unacceptable level of nitrite to investigate the possibility of contamination of samplers during transport. 3.8 laboratory blank sealed sampler drawn from the same batch as the samplers being used for NO2m

48、onitoring which is stored in a refrigerator during sampling of the exposed samplers. 3.9 repeatability condition condition of measurement, out of a set of conditions that includes the same measurement procedure, same operators, same measuring system, same operating conditions and same location, and

49、replicate measurements on the same or similar objects over a short period of time SOURCE: JGCM 200:2012 DIN EN 16339:2013-11 EN 16339:2013 (E) 7 3.10 standard (measurement) uncertainty measurement uncertainty expressed as a standard deviation SOURCE: JGCM 200:2012 3.11 uncertainty (of measurement) non-negative parameter characterizing the dispersion of the quantity values being attributed to a measurand, based on the information used Note 1 to entry: For foo