SIST EN 15259:2008
Air quality - Measurement of stationary source emissions - Requirements for measurement sections and sites and for the measurement objective, plan and report
Air quality - Measurement of stationary source emissions - Requirements for measurement sections and sites and for the measurement objective, plan and report
This European Standard specifies the following requirements:
a) requirements for measurement sections and sites with respect to performing emission measurements;
b) requirements for the measurement objective, plan and report of emission measurements of air pollutants and reference quantities to be carried out in waste gas ducts at industrial plants.
This European Standard applies to periodic measurements using manual or automated reference methods (RM).
This European Standard specifies generic principles which can be applied to perform emission measurements at different plant types and to meet different measurement objectives.
NOTE The measurement objective is specified by the customer. The testing institute identifies the measurement objective and related regulatory requirements at the beginning of the measurement planning. Where measurements are being made for regulatory purposes, the customer should seek approval from the competent authority.
This European Standard specifies procedures for taking representative samples in waste gas ducts.
This European Standard specifies a procedure for finding the best available sampling point for automated measuring systems used for continuous monitoring of emissions.
The planning and reporting aspects of this European Standard are applicable to emission measurements at diffusive and fugitive emission sources.
This European Standard does not address aspects of structural safety of chimneys and ducts, construction of working platforms and safety of personnel using them.
Luftbeschaffenheit - Messung von Emissionen aus stationären Quellen - Anforderungen an Messstrecken und Messplätze und an die Messaufgabe, den Messplan und den Messbericht
Diese Europäische Norm legt fest:
a) Mindestanforderungen für die Messstrategie, die Messplanung und den Bericht über
Emissionsmessungen von Luftverunreinigungen und Bezugsgrößen, die in Abgaskanälen von Anlagen
durchgeführt werden;
b) Mindestanforderungen für die Gestaltung und Konstruktion von Anlagen hinsichtlich der Durchführung
von Emissionsmessungen. Dies gilt insbesondere für die Anordnung, die Anzahl und die Form der
Messöffnungen und den Messplatz.
Diese Europäische Norm gilt für wiederkehrende Messungen unter Verwendung von Standardreferenz-
messverfahren (SRM) und/oder automatischen Messeinrichtungen (AMS).
Diese Europäische Norm legt allgemeine Grundsätze fest, die bei der Durchführung von Emissions-
messungen an verschiedenen Anlagentypen und bei verschiedenen Messaufgaben angewendet werden
können.
Die in dieser Europäischen Norm behandelten Aspekte der Messplanung und Berichterstattung können auf
Emissionsmessungen an diffusen Emissionsquellen sowie an Quellen flüchtiger Stoffe angewendet werden.
Qualité de l'air - Mesurage des émissions de sources fixes - Exigences relatives aux sections et aux sites de mesurage et relatives à l'objectif, au plan et au rapport de mesurage
La présente Norme européenne spécifie les exigences suivantes :
a) les exigences relatives aux sites et sections de mesurage dans le cadre de mesurages à l'émission ;
b) les exigences relatives à l'objectif, au plan et au rapport de mesurage pour les mesurages à l’émission de polluants de l'air et de grandeurs de référence à effectuer dans les conduits d'évacuation des effluents gazeux d'installations industrielles.
La présente Norme européenne s'applique aux mesurages périodiques effectués selon des méthodes de référence (RM) manuelles et automatiques.
La présente Norme européenne spécifie les principes génériques qui peuvent être appliqués pour effectuer des mesurages à l’émission à différents types d'installation et atteindre les différents objectifs de mesurage.
NOTE L'objectif de mesurage est spécifié par le client. L'institut d'essai identifie l'objectif de mesurage et les exigences réglementaires associés au début de la préparation de la campagne du mesurage. Il est recommandé que le client obtienne l'approbation préalable de l'autorité compétente, dès lors que des mesurages sont effectués à des fins réglementaires.
La présente Norme européenne spécifie les modes opératoires visant à prélever des échantillons représentatifs dans les conduits d'évacuation des effluents gazeux.
La présente Norme européenne spécifie un mode opératoire visant à déterminer le meilleur point d'échantillonnage disponible pour les systèmes automatiques de mesurage en vue de la surveillance en continu des émissions.
Les aspects relatifs à la préparation de la campagne et à l'élaboration du rapport dans la présente Norme européenne sont applicables aux mesurages à l’émission relatifs aux sources d'émission diffuses et fugitives.
La présente Norme européenne n'aborde pas les aspects relatifs à la sécurité structurelle des cheminées et des conduits, à la construction des plates-formes de travail et à la sécurité du personnel qui les utilise.
Kakovost zraka - Meritve emisije nepremičnih virov - Zahteve za merilne odseke in merilna mesta ter namen meritev, načrt meritev in poročilo o meritvah
General Information
Standards Content (Sample)
2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.WYDKLuftbeschaffenheit - Messung von Emissionen aus stationären Quellen - Anforderungen an Messstrecken und Messplätze und an die Messaufgabe, den Messplan und den MessberichtQualité de l'air - Mesurage des émissions de sources fixes - Exigences relatives aux sections et aux sites de mesurage et relatives à l'objectif, au plan et au rapport de mesurageAir quality - Measurement of stationary source emissions - Requirements for measurement sections and sites and for the measurement objective, plan and report13.040.40Stationary source emissionsICS:Ta slovenski standard je istoveten z:EN 15259:2007SIST EN 15259:2008en,fr,de01-marec-2008SIST EN 15259:2008SLOVENSKI
STANDARD
EUROPEAN STANDARDNORME EUROPÉENNEEUROPÄISCHE NORMEN 15259October 2007ICS 13.040.40 English VersionAir quality - Measurement of stationary source emissions -Requirements for measurement sections and sites and for themeasurement objective, plan and reportQualité de l'air - Mesurage des émissions de sources fixes -Exigences relatives aux sections et aux sites de mesurageet relatives à l'objectif, au plan et au rapport de mesurageLuftbeschaffenheit - Messung von Emissionen ausstationären Quellen - Anforderungen an Messstrecken undMessplätze und an die Messaufgabe, den Messplan undden MessberichtThis European Standard was approved by CEN on 18 August 2007.CEN members are bound to comply with the CEN/CENELEC Internal Regulations which stipulate the conditions for giving this EuropeanStandard the status of a national standard without any alteration. Up-to-date lists and bibliographical references concerning such nationalstandards may be obtained on application to the CEN 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 translationunder the responsibility of a CEN member into its own language and notified to the CEN Management Centre has the same status as theofficial versions.CEN members are the national standards bodies of Austria, Belgium, Bulgaria, Cyprus, Czech Republic, Denmark, Estonia, Finland,France, Germany, Greece, Hungary, Iceland, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta, Netherlands, Norway, Poland, Portugal,Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland and United Kingdom.EUROPEAN COMMITTEE FOR STANDARDIZATIONCOMITÉ EUROPÉEN DE NORMALISATIONEUROPÄISCHES KOMITEE FÜR NORMUNGManagement Centre: rue de Stassart, 36
B-1050 Brussels© 2007 CENAll rights of exploitation in any form and by any means reservedworldwide for CEN national Members.Ref. No. EN 15259:2007: ESIST EN 15259:2008
Design and construction of measurement sites.33 Annex B (informative)
Measurement planning.42 Annex C (informative)
Conversion to reference quantities.59 Annex D (normative)
Sampling strategy.62 Annex E (informative)
Examples for determining homogeneity of waste gas profiles.67 Annex F (informative)
Example form of emission measurement report.73 Annex G (informative)
Theoretical basis for the determination of the mean concentration in the measurement plane.76 Bibliography.78
According to the CEN/CENELEC Internal Regulations, the national standards organizations of the following countries are bound to implement this European Standard: Austria, Belgium, Bulgaria, Cyprus, Czech Republic, Denmark, Estonia, Finland, France, Germany, Greece, Hungary, Iceland, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta, Netherlands, Norway, Poland, Portugal, Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland and United Kingdom. SIST EN 15259:2008
The operations can be performed automatically. 3.2
individual measurement measurement carried out over a defined period of time SIST EN 15259:2008
Information on the start and end time of the measurement can be of importance, e.g. in case of parallel measurements of the reference method with an automated measuring system to be calibrated or validated. 3.3 periodic measurement determination of a measurand at specified time intervals NOTE The specified time intervals may be regular (e.g. once every month) or irregular. Measurands can include the amount or physical property of an emission. Measurements are usually made using portable equipment for typically less than 24 h. 3.4 grid measurement determination of a measurand in a given grid of measurement points in the measurement plane 3.5 measurand particular quantity subject to measurement [VIM:1993, 2.6] NOTE The measurand is a quantifiable property of the waste gas under test, for example mass concentration of a measured component, temperature, velocity, mass flow, oxygen content and water vapour content. 3.6 measured component constituent of the waste gas for which a defined measurand is to be determined by measurement 3.7 reference quantity specified physical or chemical quantity which is needed for conversion of the measurand to standard conditions NOTE Reference quantities are e.g. temperature (Tref = 273,15 K), pressure (pref = 101,325 kPa), water vapour volume fraction (href = 0 %) and oxygen volume fraction oref. 3.8 reference method RM measurement method taken as a reference by convention, which gives the accepted reference value of the measurand NOTE 1 A reference method is fully described. NOTE 2 A reference method can be a manual or an automated method. NOTE 3 Alternative methods can be used if equivalence to the reference method has been demonstrated. 3.9 standard reference method SRM reference method prescribed by European or national legislation NOTE Standard reference methods are used e.g. to calibrate and validate AMS and for periodic measurements to check compliance with limit values. 3.10 automated measuring system AMS measuring system permanently installed on site for continuous monitoring of emissions SIST EN 15259:2008
Vmc= (2) 3.27 mass flow rate m& quotient of the mass m flowing through the measurement plane and the time t tmm=& (3) 3.28 mass flow density dm& quotient of mass flow rate m& and corresponding cross-sectional area a amm&&=d (4) 3.29 sample volumetric flow volumetric flow extracted from the main stream for determination of the measured component SIST EN 15259:2008
area of the measurement plane c mass concentration d diameter of the duct dh hydraulic diameter F statistical value of the F-test hm
measured water vapour content as volume fraction href
standard water vapour content as volume fraction m mass m&
mass flow rate dm& mass flow density N number of measurements om
measured oxygen content as volume fraction oref
standard oxygen content as volume fraction P
perimeter of the measurement plane pm
measured pressure SIST EN 15259:2008
standard pressure ri
ratio of actual value yi,grid of the measurand in the grid and the value yi,ref of the reference measurement r
average of the ratios ri sgrid
standard deviation of the grid measurements sinh standard deviation due to the inhomogeneity of the waste gas spos standard deviation of combined grid and reference measurement sref
standard deviation of the reference measurements t
time Tm
measured temperature (absolute) Tref
standard temperature (absolute) Uperm
permissible expanded uncertainty Upos
expanded uncertainty of the combined grid and reference measurement Uref
expanded uncertainty related to the reference measurements at the fixed point v velocity of the gas in the measurement plane V volume V&
volume flow rate yi,grid measured value at the ith sampling point yi,ref ith measured value at the reference point 4.2 Abbreviations AMS Automated Measuring System RM Reference Method SRM Standard Reference Method SCR Selective Catalytic Reduction SNCR Selective Non Catalytic Reduction SIST EN 15259:2008
Figure 1 — Illustration of key stages of periodic measurements of emissions from stationary sources SIST EN 15259:2008
Key 1 measurement point 2 measurement line 3 measurement plane 4 measurement port 5 clearance area 6 measurement site 7 manual sampling train 8 measurement section 9 outlet section 10 inlet section
Symbols d internal duct diameter
Figure 2 — Illustration of terms related to the measurement site and measurement section
Key a)
top view b)
front view
A measurement line, measurement plane
S measurement port
S1 reference method S6 HCl, total carbon, water-vapour AMS S2 reference method
S7 reference method S3 dust AMS (optical head)
S8 volume flow AMS (transmitter) S3a dust AMS (reflector) S8a volume flow AMS (receiver) S4 SO2, NO, O2 AMS S9 temperature S5 reference method
S9a pressure Figure 3 — Example of the mounting location of measuring systems within a
measurement section at a waste gas duct (working platform not represented for simplification)
6.2 Measurement section 6.2.1 Measurement section and measurement plane The measurement section shall allow the sampling and execution of measurements at a suitable measurement plane. NOTE 1 The measurement section is the region of a conducted source (e.g. waste gas duct, stack) which includes the actual measurement plane and the inlet and outlet sections. SIST EN 15259:2008
as far downstream and upstream from any disturbance, which could produce a change in direction of flow (e.g. disturbances can be caused by bends, fans or partially closed dampers), – in a section of a duct with at least five hydraulic diameters of straight duct upstream of the sampling plane and two hydraulic diameters downstream (five hydraulic diameters from the top of a stack; see A.2) and – in a section of a duct with constant shape and cross-sectional area. NOTE 5 Effective aerodynamic arrangements (e.g. fans, vanes, ducting design) can be required to achieve mixing of the gases before entering the (straight) duct where the measurement section is located in order to get a homogeneous concentration profile at the measurement plane, especially when several gases of different characteristics in composition, coming from different installations are collected in the same duct. NOTE 6 It can be advisable to perform an exploratory velocity traverse before committing to a comprehensive installation. c) measurements at all the sampling points defined in 8.2 and Annex D shall prove that the gas stream at the measurement plane meets the following requirements: 1) angle of gas flow less than 15° with regard to duct axis; NOTE 7 A method for the determination of the angle of gas flow is given in Annex B of EN 13284-1:2001. 2) no local negative flow; 3) minimum velocity depending on the flow rate measuring method used (for Pitot tubes a differential pressure larger than 5 Pa); 4) ratio of the highest to lowest local gas velocities less than 3:1; NOTE 8 The above requirements are generally fulfilled in sections of duct with at least five hydraulic diameters of straight duct upstream of the measurement plane and two hydraulic diameters downstream (five hydraulic diameters from the top of a stack). Therefore, it is strongly recommended to design sampling locations accordingly. d) installation of measurement sections in vertical ducts should be preferred to installation in horizontal ducts; NOTE 9 At high dust concentrations, for some particle fractions, sedimentation can occur in horizontal ducts. This can lead to errors in the measurement of pollutants contained in the particle fraction, e.g. heavy metals, PCDD/PCDF. e) measurement section shall be situated where it is possible to erect suitable working platforms with the provision of the necessary infrastructure; SIST EN 15259:2008
NOTE 4 If the distance between a measurement port and the opposite interior wall of the waste gas duct is large (e.g. more than 2 m), depending on the measurement objective, two opposing measurement ports can be provided per measurement line, and the platform extended accordingly. In the case of rectangular ducts, the measurement ports should be installed on the longer side (see Figure A.6). 6.2.3 Working area and working platform 6.2.3.1 Load bearing capacity Permanent and temporary working platforms shall have a load bearing capacity sufficient to fulfil the measurement objective. NOTE Sampling can comprise of two to six persons with equipment weighing between 50 kg and 300 kg. Temporary working platforms shall be tied or supported to a permanent structure to prevent collapse or overturning. They shall be checked before use in accordance with national regulations on safety at work. 6.2.3.2 Position and working space Working platforms shall provide sufficient working area and height (working space) for the measurement objective, i.e. to manipulate the probes and operate the measuring instruments. Clearance area at the working platform shall be dimensioned appropriately. Probe introduction should not be impeded e.g. by guard fences and other built-in elements. NOTE 1 Grid measurements require a sufficiently large working area outside the waste gas duct along the measurement lines so that the measurement points can be sampled with the appropriate probes in the measurement plane. The minimum probe length depends on the internal diameter or depth of the waste gas duct and the wall thickness. NOTE 2 A sufficient depth of the working area is given by the sum of the internal diameter or depth of the waste gas duct and the wall thickness plus 1,5 m for flanged-on instruments (see A.2). If two opposite measurement ports are installed for one measurement line, a correspondingly smaller operating area depth is sufficient. NOTE 3 If the waste gas has a vertical direction of flow, both with round and rectangular waste gas ducts, a working height from the platform to the measurement lines can be established, which is approximately 1,2 m to 1,5 m. SIST EN 15259:2008
m2 m2 m2 a not needed 4 4 b 6 12 18
6.3 Measurement site 6.3.1 Power supply and equipment Power connections of an appropriate size and safeguarded in accordance with national requirement shall be installed at the measurement site. Compressed air, water connections and wastewater disposal may be necessary. 6.3.2 Safety and environmental conditions The measurement sites shall be installed in such a way as to comply with national safety at work requirements. At least the following aspects shall be considered: easy and safe access to the measurement site; transport means, for example hoists or lifts [18], to transport measuring instruments, in the case of measurement sites which are not at ground level; avoidance of area of sources which emit unexpectedly, for example rupture disks, overpressure valves or steam discharges; avoidance of any hazard by engineering or procedural measures; avoidance of areas of significant positive pressure; availability of measures to ensure personnel carrying out the emission measurements are informed of any operating faults which would endanger them; possibility to accommodate the working platform or measurement site within the plant building; protection of the working area from heat and dust; protective measures, for example weather protection and heating, to ensure the necessary environmental conditions for the personnel and the equipment used. SIST EN 15259:2008
measurements of emissions at comparable emission sources,
calculated or estimated mass flow of emissions, e.g. using data from the plant or its operation with the aid of balance sheets for individual substances and
data related to the process, e.g. knowledge of the relationship between the temperature curve of the process and emissions. Based on the information collected, the measurement objective shall be reviewed and amended, if necessary. 7.2 Measurement plan 7.2.1 Specification of measurement plan The measurement plan shall be specified on the basis of the measurement objective (see 7.1). NOTE Where measurements are being made for regulatory purposes, the customer can need approval of the measurement plan from the competent authority. In particular the following shall be specified: a) operating conditions of the plant including fuel or feedstock, waste gas components and reference quantities to be measured; b) timing and siting arrangements of the required individual measurements and measurement dates; c) measurement methods to be applied; d) measurement sections and measurement sites; e) technical supervisor, necessary personnel and auxiliary help for carrying out of the measurements; f) reporting arrangements. 7.2.2 Plant operating conditions and load characteristics The operating conditions of the plant, waste gas composition and reference quantities to be measured shall be specified in accordance with the measurement objective. The influence of the mode of plant operation, the feed materials, and the waste gas cleaning system in the plant on the emission shall be considered (examples are given in B.1). NOTE 1 An essential feature of the specification is the maximum plant output. This determines, for example,
in the case of combustion plants, the size and shape of the combustion space, the number of burners or number of transporters for combustible matter and the amount of combustible matter which can be fed and SIST EN 15259:2008
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