SIST EN 14211:2005
(Main)Ambient air quality - Standard method for the measurement of the concentration of nitrogen dioxide and nitrogen monoxide by chemiluminescence
Ambient air quality - Standard method for the measurement of the concentration of nitrogen dioxide and nitrogen monoxide by chemiluminescence
This document specifies a continuous measurement method for the determination of the concentration of nitrogen dioxide and nitrogen monoxide present in ambient air based on the chemiluminescence measuring principle. This document describes the performance characteristics and sets the relevant minimum criteria required to select an appropriate chemiluminescence analyser by means of type approval tests. It also includes the evaluation of the suitability of an analyser for use in a specific fixed site so as to meet the Directives data quality requirements and requirements during sampling, calibration and quality assurance.
The method is applicable to the determination of the concentration of nitrogen dioxide present in ambient air from 0 mg/m3 to 500 mg/m3. This concentration range represents the certification range for NO2 for the type approval test.
NOTE 1 0 mg/m3 to 500 mg/m3 of NO2 corresponds to 0 nmol/mol to 261 nmol/mol of NO2.
The method is applicable to the determination of the concentration of nitrogen monoxide present in ambient air from 0 mg/m3 to 1 200 mg/m3. This concentration range represents the certification range for NO for the type approval test.
NOTE 2 0 mg/m3 to 1 200 mg/m3 of NO corresponds to 0 nmol/mol to 962 nmol/mol of NO.
The method covers the determination of ambient air concentrations of nitrogen dioxide and nitrogen monoxide in zones classified as rural areas, urban-background areas and traffic-orientated locations.
NOTE 3 Lower ranges may be used for measurement systems applied at rural locations monitoring Ecosystems.
The results are expressed in mg/m3 (at 293 K and 101,3 kPa).
When the standard is used for other purposes than the EU Directive, the range and uncertainty requirements need not apply.
Luftqualität - Messverfahren zur Bestimmung der Konzentration von Stickstoffdioxid und Stickstoffmonoxid mit Chemilumineszenz
Dieses Dokument legt ein kontinuierliches Messverfahren zur Bestimmung der Konzentration von Stickstoffdioxid und Stickstoffmonoxid in Luft nach dem Chemilumineszenz-Messprinzip fest. Dieses Dokument gibt die Leistungskenngrößen an und legt die relevanten Mindestanforderungen für die Eignungsprüfung von Ultraviolett-Fluoreszenz-Messgeräten fest. Es schließt auch die Bewertung der Eignung eines Messgeräts zur Anwendung an einer spezifischen Messstelle im Hinblick auf die Daten-qualitätsanforderungen der EU-Richtlinien ein und enthält Anforderungen für die Probenahme, Kalibrierung und Qualitätssicherung bei der Anwendung.
Das Verfahren ist anwendbar zur Bestimmung der Massenkonzentration von Stickstoffdioxid in Luft im Bereich von 0 µg/m3 bis 500 µg/m3. Dieser Konzentrationsbereich entspricht dem Zertifizierungsbereich für die Eignungsprüfung.
ANMERKUNG 1 0 mg/m3 bis 500 mg/m3 an NO2 entsprechen 0 nmol/mol bis 261 nmol/mol an NO2.
Das Verfahren ist anwendbar zur Bestimmung der Massenkonzentration von Stickstoffmonoxid in Luft im Bereich von 0 µg/m3 bis 1200 µg/m3. Dieser Konzentrationsbereich entspricht dem Zertifizierungsbereich für die Eignungsprüfung.
ANMERKUNG 2 0 mg/m3 bis 1 200 mg/m3 an NO entsprechen 0 nmol/mol bis 962 nmol/mol an NO.
Das Verfahren umfasst die Bestimmung der Konzentration von Stickstoffdioxid und Stickstoffmonoxid in Gebieten, die als ländliche Gebiete, Gebiete mit städtischem Hintergrund und verkehrsbezogene Standorte klassifiziert sind.
ANMERKUNG 3 Kleinere Bereiche können für Messsysteme an ländlichen Standorten zur Überwachung von Ökosystemen verwendet werden.
Die Ergebnisse werden in µg/m3 (bei 293 K und 101,3 kPa) angegeben.
Wenn diese Norm für andere als in der EU-Richtlinie festgelegte Zwecke eingesetzt wird, müssen die Anforderungen hinsichtlich Anwendungsbereich und Unsicherheit nicht gestellt werden.
Qualité de l'air ambiant - Méthode normalisée pour le mesurage de la concentration en dioxyde d'azote et en monoxyde d'azote par chimiluminescence
Le présent document spécifie une méthode de mesurage en continu pour la détermination de la concentration en dioxyde d'azote et en monoxyde d'azote dans l'air ambiant, selon le principe de mesure par chimiluminescence. Le présent document décrit les caractéristiques de performance et fixe les criteres minimums requis pour sélectionner un analyseur par chimiluminescence approprié a l'aide d'essais d'approbation de type. Il présente également l'évaluation de l'aptitude a l'emploi d'un analyseur sur un site fixe spécifique de maniere a répondre aux exigences de qualité des données prescrites dans les Directives ainsi qu'aux exigences a observer au cours du prélevement, de l'étalonnage et de l'assurance qualité.
La méthode s'applique a la détermination de la concentration en dioxyde d'azote présent dans l'air ambiant dans une plage comprise entre 0 mg/m3 et 500 mg/m3. Cette plage de concentration représente l'étendue de mesure certifiée de NO2 pour l'essai d'approbation de type.
NOTE 1 La plage comprise entre 0 mg/m3 et 500 mg/m3 de NO2 correspond a la plage de 0 nmol/mol a 261 nmol/mol de NO2.
La méthode s'applique a la détermination de la concentration en monoxyde d'azote présent dans l'air ambiant dans une plage comprise entre 0 mg/m3 et 1 200 mg/m3. Cette plage de concentration représente l'étendue de mesure certifiée de NO pour l'essai d'approbation de type.
NOTE 2 La plage comprise entre 0 mg/m3 et 1 200 mg/m3 de NO correspond a la plage de 0 nmol/mol a 962 nmol/mol de NO.
La méthode couvre la détermination des concentrations en dioxyde d'azote et en monoxyde d'azote présents dans l'air ambiant dans les zones classées comme zones rurales, périurbaines et proches d'axes de circulation automobile.
NOTE 3 Des plages inférieures peuvent etre utilisées pour les systemes de mesure appliqués aux zones rurales contrôlant des écosystemes.
Les résultats sont exprimés en mg/m3 (a 293 K et 101,3 kPa).
Lorsque la norme est utilisée a d'autres fins que la Directive UE,
Kakovost zunanjega zraka – Standardna metoda za določanje koncentracije dušikovega dioksida in dušikovega monoksida s kemiluminiscenco
General Information
Relations
Standards Content (Sample)
SLOVENSKI STANDARD
SIST EN 14211:2005
01-september-2005
.DNRYRVW]XQDQMHJD]UDND±6WDQGDUGQDPHWRGD]DGRORþDQMHNRQFHQWUDFLMH
GXãLNRYHJDGLRNVLGDLQGXãLNRYHJDPRQRNVLGDVNHPLOXPLQLVFHQFR
Ambient air quality - Standard method for the measurement of the concentration of
nitrogen dioxide and nitrogen monoxide by chemiluminescence
Luftqualität - Messverfahren zur Bestimmung der Konzentration von Stickstoffdioxid und
Stickstoffmonoxid mit Chemilumineszenz
Qualité de l'air ambiant - Méthode normalisée pour le mesurage de la concentration en
dioxyde d'azote et en monoxyde d'azote par chimiluminescence
Ta slovenski standard je istoveten z: EN 14211:2005
ICS:
13.040.20 Kakovost okoljskega zraka Ambient atmospheres
SIST EN 14211:2005 en,fr,de
2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.
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SIST EN 14211:2005
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SIST EN 14211:2005
EUROPEAN STANDARD
EN 14211
NORME EUROPÉENNE
EUROPÄISCHE NORM
March 2005
ICS 13.040.20
English version
Ambient air quality - Standard method for the measurement of
the concentration of nitrogen dioxide and nitrogen monoxide by
chemiluminescence
Qualité de l'air ambiant - Méthode normalisée pour le Luftqualität - Messverfahren zur Bestimmung der
mesurage de la concentration en dioxyde d'azote et Konzentration von Stickstoffdioxid und Stickstoffmonoxid
monoxyde d'azote par chimiluminescence mit Chemilumineszenz
This European Standard was approved by CEN on 10 December 2004.
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 references concerning such national
standards may be obtained on application to the Central Secretariat 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 CEN member into its own language and notified to the Central Secretariat has the same status as the official
versions.
CEN members are the national standards bodies of Austria, Belgium, Cyprus, Czech Republic, Denmark, Estonia, Finland, France,
Germany, Greece, Hungary, Iceland, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta, Netherlands, Norway, Poland, Portugal, Slovakia,
Slovenia, Spain, Sweden, Switzerland and United Kingdom.
EUROPEAN COMMITTEE FOR STANDARDIZATION
COMITÉ EUROPÉEN DE NORMALISATION
EUROPÄISCHES KOMITEE FÜR NORMUNG
Management Centre: rue de Stassart, 36 B-1050 Brussels
© 2005 CEN All rights of exploitation in any form and by any means reserved Ref. No. EN 14211:2005: E
worldwide for CEN national Members.
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SIST EN 14211:2005
EN 14211:2005 (E)
Contents
Page
Foreword.4
1 Scope .5
2 Normative references .5
3 Terms and definitions .6
4 Symbols and abbreviated terms .10
5 Principle.12
5.1 General.12
5.2 Measuring principle.13
5.3 Type approval test .13
5.4 Field operation and quality control.14
6 Sampling equipment .14
6.1 General.14
6.2 Sampling location.14
6.3 Sample inlet and sampling line .14
6.4 Particulate filter.15
6.5 Control and regulation of sample flow rate .15
6.6 Sampling pump for the manifold.15
7 Analyser equipment .16
7.1 General.16
7.2 Converter .16
7.3 Ozone generator .16
7.4 Reaction chamber.17
7.5 Optical filter .17
7.6 Detector .17
7.7 Ozone removal device.17
7.8 Sampling pump for the analyser.17
7.9 Residence time inside the analyser.17
8 Type approval of nitrogen dioxide and nitrogen monoxide analysers .17
8.1 General.17
8.2 Relevant performance characteristics and performance criteria .18
8.3 Design change .20
8.4 Procedures for determination of the performance characteristics during the laboratory test .21
8.5 Determination of the performance characteristics during the field test.32
8.6 Expanded uncertainty calculation for type approval.36
9 Field operation and ongoing quality control .36
9.1 General.36
9.2 Suitability evaluation.37
9.3 Initial installation.38
9.4 Ongoing quality control .38
9.5 Calibration of the analyser.40
9.6 Checks .41
9.7 Maintenance .44
9.8 Data handling and data reports.44
10 Expression of results .45
11 Test reports and documentation.45
11.1 Type approval test .45
2
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EN 14211:2005 (E)
11.2 Field operation .45
Annex A (normative) Calculation of residence times for a maximum allowable NO increase in the
2
sampling line [ISO 13964] .47
Annex B (normative) Test of lack of fit.48
Annex C (informative) Sampling equipment.50
Annex D (informative) Sampling on microscale [2] .52
Annex E (informative) Types of chemiluminescence analysers.53
Annex F (informative) Manifold testing equipment.56
Annex G (normative) Type approval.57
Annex H (normative) Calculation of uncertainty in field operation at the hourly limit value .76
Annex I (normative) Calculation of uncertainty in field operation at the annual limit value .82
Bibliography.92
3
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SIST EN 14211:2005
EN 14211:2005 (E)
Foreword
This document (EN 14211:2005) 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 September 2005, and conflicting national standards shall be withdrawn at the
latest by September 2005.
According to the CEN/CENELEC Internal Regulations, the national standards organizations of the following
countries are bound to implement this European Standard: Austria, Belgium, Cyprus, Czech Republic, Denmark,
Estonia, Finland, France, Germany, Greece, Hungary, Iceland, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta,
Netherlands, Norway, Poland, Portugal, Slovakia, Slovenia, Spain, Sweden, Switzerland and United Kingdom.
4
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SIST EN 14211:2005
EN 14211:2005 (E)
1 Scope
This document specifies a continuous measurement method for the determination of the concentration of nitrogen
dioxide and nitrogen monoxide present in ambient air based on the chemiluminescence measuring principle. This
document describes the performance characteristics and sets the relevant minimum criteria required to select an
appropriate chemiluminescence analyser by means of type approval tests. It also includes the evaluation of the
suitability of an analyser for use in a specific fixed site so as to meet the Directives data quality requirements and
requirements during sampling, calibration and quality assurance.
The method is applicable to the determination of the concentration of nitrogen dioxide present in ambient air from
3 3
0 µg/m to 500 µg/m . This concentration range represents the certification range for NO for the type approval test.
2
3 3
NOTE 1 0 µg/m to 500 µg/m of NO corresponds to 0 nmol/mol to 261 nmol/mol of NO .
2 2
The method is applicable to the determination of the concentration of nitrogen monoxide present in ambient air
3 3
from 0 µg/m to 1 200 µg/m . This concentration range represents the certification range for NO for the type
approval test.
3 3
NOTE 2 0 µg/m to 1 200 µg/m of NO corresponds to 0 nmol/mol to 962 nmol/mol of NO.
The method covers the determination of ambient air concentrations of nitrogen dioxide and nitrogen monoxide in
zones classified as rural areas, urban-background areas and traffic-orientated locations.
NOTE 3 Lower ranges may be used for measurement systems applied at rural locations monitoring Ecosystems.
3
The results are expressed in µg/m (at 293 K and 101,3 kPa).
When the standard is used for other purposes than the EU Directive, the range and uncertainty requirements need
not apply.
2 Normative references
The following referenced documents are indispensable for the application of this document. For dated references,
only the edition cited applies. For undated references, the latest edition of the referenced document (including any
amendments) applies.
ENV 13005, Guide to the expression of uncertainty in measurement
EN ISO 14956, Air quality — Evaluation of the suitability of a measurement procedure by comparison with a
required measurement uncertainty (ISO 14956:2002)
ISO 6142, Gas analysis — Preparation of calibration gas mixtures — Gravimetric method
ISO 6143, Gas analysis — Comparison methods for determining and checking the composition of calibration gas
mixtures
ISO 6144, Gas analysis — Preparation of calibration gas mixtures — Static volumetric method
ISO 6145 (all parts), Gas analysis — Preparation of calibration gas mixtures using dynamic volumetric methods
ISO 13964:1998, Air quality — Determination of ozone in ambient air — Ultraviolet photometric method
5
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EN 14211:2005 (E)
3 Terms and definitions
For the purpose of this document, the following terms and definitions apply.
3.1
ambient air
1
outdoor air in the troposphere, excluding workplace air
3.2
sample gas temperature
temperature at the sample inlet outside the monitoring station
3.3
availability of the analyser
fraction of the total time period for which usually valid measuring data of the ambient air concentration is available
from an analyser
3.4
certification range
concentration range for which the analyser is type approved
3.5
calibration
comparison of the analyser response to a known gas concentration with a known uncertainty
3.6
combined standard uncertainty
calculation result of combining the uncertainties determined from all performance characteristics specified in this
document according to the prescribed procedures given in this document
3.7
converter efficiency
degree of conversion of NO present in the sample gas into NO, given as a percentage
2
3.8
coverage factor
numerical factor used as a multiplier of the combined standard uncertainty in order to obtain an expanded
uncertainty
3.9
designated body
body which has been designated for a specific task (type approval tests and/or QA/QC activities in the field) by the
competent authority in the Member States
NOTE It is recommended that the designated body is accredited for the specific task according to EN ISO/IEC 17025.
3.10
expanded uncertainty
quantity defining an interval about the result of a measurement that may be expected to encompass a large fraction
of the distribution of values that could reasonably be attributed to the measurand
NOTE for the purpose of this document the expanded uncertainty is the combined standard uncertainty multiplied by a
coverage factor k = 2 resulting in an interval with a level of confidence of 95 %
1
As stated in the relevant EU legislation.
6
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3.11
fall time
difference between the response time (fall) and the lag time (fall)
3.12
independent measurement
individual measurement that is not influenced by a previous individual measurement by separating two individual
measurements by at least four response times
3.13
individual measurement
measurement averaged over a time period equal to the response time of the analyser
3.14
influence quantity
quantity that is not the measurand but that affects the result of the measurement (VIM 2.7), either an interferent
influence quantity (i.e. the concentration of a substance in the air under investigation that is not the measurand), or
an external influence quantity (i.e. a quantity that is not the measurand nor the concentration of a substance in the
air mass under investigation)
NOTE Examples are:
presence of interfering gases in the flue gas matrix (interferent influence quantity);
temperature of the surrounding air (external influence quantity);
atmospheric pressure (external influence quantity);
pressure of the gas sample (external influence quantity).
3.15
interference
response of the analyser to interferents
3.16
interferent
component of the air sample, excluding the measured constituent, that effects the output signal
3.17
lag time
time interval from the instant at which a step change of sample concentration occurs at the inlet of the analyser to
the instant at which the output reading reaches a level corresponding to 10 % of the stable output reading
3.18
lag time (fall)
lag time for a negative step change
3.19
lag time (rise)
lag time for a positive step change
3.20
limit value
level fixed on the basis of scientific knowledge, with the aim of avoiding, preventing or reducing harmful effects on
human health and/or the environment as a whole, to be attained within a given period and not to be exceeded once
attained
3.21
lack of fit
maximum deviation of the average of a series of measurements at the same concentration from the linear
regression line
7
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3.22
long term drift
difference between zero or span readings over a determined period of time (e.g. period of unattended operation)
3.23
monitoring station
enclosure located in the field in which an NO analyser has been installed to monitor nitrogen monoxide and
x
dioxide concentrations in such a way that its performance and operation complies with the prescribed requirements
3.24
parallel measurement
measurements from different analysers, sampling from one and the same sampling manifold starting at the same
time and ending at the same time
3.25
performance characteristic
one of the parameters assigned to equipment in order to define its performance
3.26
performance criterion
limiting quantitative numerical value assigned to a performance characteristic, to which conformance is tested
3.27
period of unattended operation
time period over which the drift is within the performance criterion for long term drift
3.28
repeatability (of results of measurement)
closeness of the agreement between the results of successive individual measurements of the same measurand
carried out under the same conditions of measurement [1]
NOTE These conditions are called laboratory repeatability conditions and include:
- the same measurement procedure;
- the same observer;
- the same analyser, used under the same conditions;
- at the same location;
- repetition over a short period of time.
3.29
reproducibility under field conditions
closeness of the agreement between the results of simultaneous measurements with two analysers in ambient air
carried out under the same conditions of measurement
NOTE These conditions are called field reproducibility conditions and include:
- the same measurement procedure;
- two identical analysers, used under the same conditions;
- at the same monitoring station;
- the period of unattended operation.
3.30
residence time inside the analyser
time period for the sampled air to be transported from the inlet of the analyser to the reaction chamber for the
NO-channel
3.31
residence time in the sampling system
time period for the sampled air to be transported from the sampling inlet (of the sampling system) to the inlet of the
analyser
8
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3.32
response time
time interval from the instant at which a step change of sample concentration occurs at the inlet of the analyser to
the instant at which the output reading reaches a level corresponding to 90 % of the stable output reading
3.33
response time (fall)
response time to a negative step change
NOTE Response time (fall) is the sum of the lag time (fall) and the fall time.
3.34
response time (rise)
response time to a positive step change
NOTE Response time (rise) is the sum of the lag time (rise) and the rise time.
3.35
rise time
difference between the response time (rise) and the lag time (rise)
3.36
sampled air
ambient air that has been sampled through the sampling inlet and sampling system
3.37
sampling inlet
entrance to the sampling system where ambient air is collected from the atmosphere
3.38
short-term drift
difference between zero or span readings at the beginning and end of a 12 h period
3.39
standard uncertainty
uncertainty of the result of a measurement expressed as a standard deviation
[ENV 13005]
3.40
surrounding temperature
temperature of the air directly surrounding the analyser (temperature inside the monitoring station or laboratory)
3.41
total residence time
sum of the residence time in the sampling system and the residence time inside the analyser
3.42
type approval
decision taken by a designated body that the pattern of an analyser conforms to the requirements as laid down in
this document
3. 43
type approval test
examination of two or more analysers of the same pattern which are submitted by a manufacturer to a designated
body including the tests necessary for approval of the pattern
9
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3.44
uncertainty (of measurement)
parameter associated with the result of a measurement that characterises the dispersion of the values that could
be attributed to the measureand
4 Symbols and abbreviated terms
For the purposes of this document, the following symbols and abbreviated terms apply.
A availability of the analyser
a
Av average concentration of the measurand during the field test
b sensitivity coefficient of the analyser to sample gas pressure change
gp
b sensitivity coefficient of the analyser to sample gas temperature change
gt
b sensitivity coefficient of the analyser to surrounding air temperature change
st
b sensitivity coefficient of the analyser to electrical voltage change
V
C NO concentration of the applied gas
C average concentration of the measurements at sampling gas pressure P1
P1
C average concentration of the measurements at sampling gas pressure P2
P2
C average concentration of the measurements at span level at the beginning of the drift period
s,1
C average concentration of the measurements at span level at the end of the drift period
s,2
c test gas concentration
t
C average concentration of the measurements at sample gas temperature T
T1 1
C average concentration of the measurements at sample gas temperature T
T2 2
C average concentration reading of the measurements at voltage V
V1 1
C average concentration reading of the measurements at voltage V
V2 2
C average concentration of the measurements at zero at the beginning of the drift period
z,1
C average concentration of the measurements at zero at the end of the drift period
z,2
av
average of at least four independent measurements during the constant concentration period (t )
c
C
const
av
average of at least four independent measurements during the variable concentration period (t )
v
C
var
average difference of parallel measurements
d
f
d the ith difference in a parallel measurement
f,i
D long-term drift at span concentration c
l,s t
10
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D long-term drift at zero
l,z
D short-term drift at span level
s,s
D short-term drift at zero
s,z
D difference sample/calibration port
sc
E converter efficiency
conv
E sample system collection efficiency
ss
F response factor in concentration units per voltage output of the analyser
r
P sampling gas pressure P
1 1
P sampling gas pressure P
2 2
R mean analyser response to the test gas directly sampled by the analyser
d
R mean analyser response to the test gas via the sample manifold
m
s repeatability standard deviation at zero
r,z
s repeatability standard deviation at concentration c
r,ct t
s reproducibility standard deviation under field conditions
r,f
s repeatability standard deviation
l
T surrounding air temperature
T surrounding air temperature at the laboratory
l
T sample gas temperature T
1 1
T sample gas temperature T
2 2
t relative difference between response time (rise) and response time (fall)
d
t response time (fall)
f
t response time (rise)
r
t time period of the field test minus the time for calibration, conditioning and maintenance
t
t total time period with validated measuring data
u
t whole number of t and t pairs
V NO zero
V minimum voltage V (V) specified by the manufacturer
1 min
V maximum voltage V (V) specified by the manufacturer
2 max
average of measurements
x
x first average of the measurements at T just after calibration
1 l
11
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EN 14211:2005 (E)
x average of the measurements at zero
z
x second average of the measurements at T just before calibration
2 l
x average of the measurements at concentration c
ct t
X averaging effect
av
x average of the measurements using the calibration port
c
X influence quantity of CO with concentration 500 µmol/mol
CO2,z,ct 2
X influence quantity of H O with concentration 19 mmol/mol
H2O,z,ct 2
x the ith measurement
i
influence quantity of the interferent at concentration c
X
t
int,ct
X influence quantity of the interferent at zero
int,z
X largest residual from the linear regression function at concentrations higher than zero
l
X residual from the linear regression function at zero concentration
l,z
X influence quantity of NH with concentration 200 nmol/mol
NH3,z,ct 3
X influence quantity of O with concentration 200 nmol/mol
O3,z,ct 3
x average of the measurements using the sample port
s
X difference between the readings of two consecutive span checks
s
x average of the measurements at T or T
T min max
X difference between the readings of the recent zero check and the most recent calibration
z
(x ) the ith measurement result of analyser 1;
1,f i
(x ) the ith measurement result of analyser 2 at the same time as the measurement of analyser 1;
2,f i
Z reading of the first zero check
1
Z reading of the second zero check
2
∆P measured pressure drop induced by the manifold pump
m
∆R change in the analyser’s response due to the influence of the pressure drop induced by the manifold
a
pump, expressed as a percentage
5 Principle
5.1 General
This document describes the method for measurement of the concentrations of nitrogen dioxide and nitrogen
monoxide in ambient air by means of chemiluminescence. The requirements, the specific components of the
chemiluminescence analyser and its sampling system are described. A number of performance characteristics with
associated minimum performance criteria are given for the analyser. The actual values of these performance
characteristics for a specific type of analyser shall be determined in a so-called type approval test for whi
...
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