SIST EN 13890:2003
(Main)Workplace atmospheres - Procedures for measuring metals and metalloids in airborne paticles - Requirements and test methods
Workplace atmospheres - Procedures for measuring metals and metalloids in airborne paticles - Requirements and test methods
This European Standard specifies performance requirements and test methods for procedures for measuring metals and metalloids in airborne particles collected on a suitable substrate, e.g. a filter.
Arbeitsplatzatmosphäre - Verfahren zur quantitativen Bestimmung von Metallen und Metalloiden in Schwebstoffen - Anforderungen und Prüfverfahren
Diese Europäische Norm legt Leistungsanforderungen und Prüfverfahren für Verfahren zur quantitativen Bestimmung von Metallen und Metalloiden in Schwebstoffen fest, die auf einem geeigneten Substrat, z.B. einem Filter, gesammelt wurden.
Atmospheres des lieux de travail - Procédures de mesurage des métaux et métalloides dans les particules en suspension dans l'air - Exigences et méthodes d'essai
La présente Norme européenne précise les exigences de performance et les méthodes d'essai pour l'évaluation des procédures de mesurage des métaux et métalloides présents dans les particules en suspension dans l'air recueillies sur un substrat approprié, par exemple un filtre.
La présente Norme européenne ne s'applique pas aux procédures de mesurage des métaux ou métalloides présents dans des gaz ou des vapeurs inorganiques, par exemple le mercure, l'arsine, etc. (voir l'EN 838 [1] et l'EN 1076 [2]), ni aux procédures de mesurage des métaux et métalloides présents dans des composés pouvant exister sous forme de mélange de particules/vapeurs, par exemple le trioxyde d'arsenic (voir l'ENV 13936 [3]).
La présente Norme européenne s'applique aux procédures de mesurage qui dissocient l'étape d'échantillonnage de l'étape d'analyse, mais elle ne précise aucune exigence métrologique concernant la collecte, le transport et le stockage des échantillons, dans la mesure ou ces exigences sont traitées dans l'EN 13205.
La présente Norme européenne prescrit une méthode permettant de déterminer l'erreur systématique (ou biais) et la fidélité de la méthode d'analyse ainsi que de combiner celle-ci au biais et a la fidélité de la méthode d'échantillonnage afin d'estimer l'incertitude globale de la procédure de mesurage dans son ensemble.
En l'absence de procédure de mesurage d'un métal ou métalloide particulier satisfaisant aux exigences de la présente Norme européenne, il est recommandé d'utiliser une procédure de mesurage dont les performances sont les plus proches possibles des exigences spécifiées.
Zrak na delovnem mestu - Postopki za merjenje kovin in polkovin v lebdečih delcih - Zahteve in preskusne metode
General Information
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Standards Content (Sample)
SLOVENSKI STANDARD
SIST EN 13890:2003
01-marec-2003
=UDNQDGHORYQHPPHVWX3RVWRSNL]DPHUMHQMHNRYLQLQSRONRYLQYOHEGHþLKGHOFLK
=DKWHYHLQSUHVNXVQHPHWRGH
Workplace atmospheres - Procedures for measuring metals and metalloids in airborne
paticles - Requirements and test methods
Arbeitsplatzatmosphäre - Verfahren zur quantitativen Bestimmung von Metallen und
Metalloiden in Schwebstoffen - Anforderungen und Prüfverfahren
Atmospheres des lieux de travail - Procédures de mesurage des métaux et métalloides
dans les particules en suspension dans l'air - Exigences et méthodes d'essai
Ta slovenski standard je istoveten z: EN 13890:2002
ICS:
13.040.30 Kakovost zraka na delovnem Workplace atmospheres
mestu
SIST EN 13890:2003 en,fr,de
2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.
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SIST EN 13890:2003
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SIST EN 13890:2003
EUROPEAN STANDARD
EN 13890
NORME EUROPÉENNE
EUROPÄISCHE NORM
October 2002
ICS 13.040.30
English version
Workplace atmospheres - Procedures for measuring metals and
metalloids in airborne paticles - Requirements and test methods
Atmosphères des lieux de travail - Procédures de Arbeitsplatzatmosphäre - Verfahren zur quantitativen
mesurage des métaux et métalloïdes dans les particules en Bestimmung von Metallen und Metalloiden in
suspension dans l'air - Exigences et méthodes d'essai Schwebstoffen - Anforderungen und Prüfverfahren
This European Standard was approved by CEN on 9 September 2002.
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 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 CEN member into its own language and notified to the Management Centre has the same status as the official
versions.
CEN members are the national standards bodies of Austria, Belgium, Czech Republic, Denmark, Finland, France, Germany, Greece,
Iceland, Ireland, Italy, Luxembourg, Malta, Netherlands, Norway, Portugal, 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
© 2002 CEN All rights of exploitation in any form and by any means reserved Ref. No. EN 13890:2002 E
worldwide for CEN national Members.
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SIST EN 13890:2003
EN 13890:2002 (E)
Contents
page
Foreword.4
Introduction .5
1 Scope .5
2 Normative references .5
3 Terms and definitions.6
3.1 EN 1540 definitions.6
3.2 Measurement terms .6
3.3 Sampling terms .6
3.4 Statistical terms .7
4 Principle.8
5 Requirements .8
5.1 General requirements.8
5.1.1 Scope of the measuring procedure.8
5.1.2 Method performance .8
5.1.3 Safety information .9
5.1.4 Samplers.9
5.1.5 Sampling pumps .9
5.1.6 Quantification limit .9
5.1.7 Other detailed requirements.9
5.2 Analytical recovery .9
5.3 Overall uncertainty .9
6 Reagents.9
7 Reference samples .10
7.1 Standard solutions .10
7.2 Reference materials.10
7.3 Reference air samples.10
8 Apparatus .10
9 Test methods.11
9.1 Detection limits and quantification limits.11
9.1.1 Determination of detection limits and quantification limits .11
9.1.2 Comparison of results with the acceptance criteria .11
9.2 Selection of test methods for determination of analytical bias and precision.11
9.3 Analytical bias.11
9.3.1 Consideration of the analytical bias of procedures for soluble metals and metalloids.11
9.3.2 Determination of the analytical bias of procedures that involve sample dissolution or
dispersion of the collected airborne particles in a liquid .11
9.4 Analytical precision .12
9.4.1 Determination of the analytical precision of procedures that involve sample transformation
prior to analysis .12
9.4.2 Estimation of the analytical precision of procedures that do not involve sample transformation.13
9.5 Estimation of overall uncertainty .13
10 Test report .14
Annex A (informative) Guidance on selection of test methods.15
Annex B (informative) Guidance on determination of analytical bias .16
B.1 Determination of the analytical bias of procedures that involve sample dissolution .16
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B.2 Determination or estimation of the analytical bias of procedures that do not involve a sample
transformation.16
Annex C (informative) Example of estimation of overall uncertainty .17
Annex D (informative) Estimation of overall uncertainty .19
D.1 General performance requirements for measurement of chemical agents in air .19
D.2 Combination of sampler bias and analytical bias .20
D.3 Combination of sampling and analytical precision.20
Consideration of sampler bias and analytical bias .20
D.4.1 Sampler bias.20
D.4.2 Sampling precision.21
D.5 Estimation of overall uncertainty.21
D.5.1 General case.21
D.5.2 Estimation of overall uncertainty of procedures for measuring metals and metalloids in
inhalable dust.21
D.5.3 Estimation of overall uncertainty of procedures for measuring metals and metalloids in
respirable dust .22
Bibliography .23
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EN 13890:2002 (E)
Foreword
This document EN 13890:2002 has been prepared by Technical Committee CEN/TC 137 "Assessment of
workplace exposure", 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 April 2003, and conflicting national standards shall be withdrawn at the latest by
April 2003.
Annexes A, B, C and D are informative.
According to the CEN/CENELEC Internal Regulations, the national standards organizations of the following
countries are bound to implement this European Standard: Austria, Belgium, Czech Republic, Denmark, Finland,
France, Germany, Greece, Iceland, Ireland, Italy, Luxembourg, Malta, Netherlands, Norway, Portugal, Spain,
Sweden, Switzerland and the United Kingdom.
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Introduction
EN 482 prescribes general requirements for the performance of procedures for measuring chemical agents in
workplace atmospheres. These requirements include maximum values of overall uncertainty (a combination of
precision and bias) achievable under prescribed laboratory conditions.
This European Standard provides a framework for assessing the performance of procedures for measuring metals
and metalloids against the criteria specified in EN 482. It enables producers and users of procedures for measuring
metals and metalloids in airborne particles to adopt a consistent approach to method validation.
1 Scope
This European Standard specifies performance requirements and test methods for the evaluation of procedures for
measuring metals and metalloids in airborne particles collected on a suitable substrate, e.g. a filter.
This European Standard is not applicable to procedures for measuring metals or metalloids present in inorganic
gases or vapours, e.g. mercury, arsine, etc (see EN 838 [1] and EN 1076 [2]), or to procedures for measuring
metals and metalloids in compounds that could be present as a particle/vapour mixture, e.g. arsenic trioxide (see
ENV 13936 [3]).
This European Standard is applicable to measuring procedures in which sampling and analysis is carried out in
separate stages, but it does not specify performance requirements for collection, transport and storage of samples,
since these are dealt with in EN 13205.
This European Standard specifies a method for determining the bias and precision of the analytical method and
combining this with the bias and precision of the sampling method to estimate the overall uncertainty of the
measuring procedure as a whole.
If there is no procedure for measuring a particular metal or metalloid which meets the requirements of this
European Standard, it is recommended to use a measuring procedure whose performance is nearest to the
specified requirements.
2 Normative references
This European Standard incorporates by dated or undated reference, provisions from other publications. These
normative references are cited at the appropriate places in the text, and the publications are listed hereafter. For
dated references, subsequent amendments to or revisions of any of these publications apply to this European
Standard only when incorporated in it by amendment or revision. For undated references the latest edition of the
publication referred to applies (including amendments).
EN 481, Workplace atmospheres — Size fraction definitions for measurement of airborne particles.
EN 482:1994, Workplace atmospheres — General requirements for the performance of procedures for the
measurement of chemical agents.
EN 1232, Workplace atmospheres — Pumps for personal sampling of chemical agents — Requirements and test
methods.
EN 1540, Workplace atmospheres — Terminology.
EN 12919, Workplace atmospheres — Pumps for the sampling of chemical agents with a volume flow rate of over
5 l/min — Requirements and test methods.
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EN 13205:2001, Workplace atmospheres — Assessment of performance of instruments for measurement of
airborne particle concentrations.
EN ISO 3696, Water for analytical laboratory use — Specification and test methods (ISO 3696:1987).
3 Terms and definitions
For the purposes of this European Standard, the following terms and definitions apply.
3.1 EN 1540 definitions
Averaging time, bias, chemical agent, limit value, measuring procedure, overall uncertainty, precision, specified
measuring range, true value, validation:
Definitions for these terms are as in EN 1540.
3.2 Measurement terms
3.2.1
analysis
all operations carried out after sample preparation to determine the amount or concentration of the metals or
metalloids of interest present in the sample
3.2.2
analytical method
all steps of the measuring procedure that describe the overall process of sample preparation and analysis
3.2.3
sampling method
all steps of the measuring procedure that describe the process of collecting an air sample
3.2.4
sample preparation
all operations carried out on a sample, after transportation and storage, to prepare it for analysis, including
transformation of the sample into a measurable state, where necessary
3.2.5
sample dissolution
process of obtaining a solution containing the analytes of interest from a sample.
NOTE This can or cannot involve complete dissolution of the sample.
3.2.6
reference sample
sample having a known or measured content or loading of the metals and metalloids of interest, which is analysed
to determine the analytical bias or the analytical precision of a measuring procedure
3.2.7
test solution
solution prepared by the process of sample dissolution and subjected to any further operations required to bring it
into a state in which it is ready for analysis
3.3 Sampling terms
3.3.1
collection substrate
medium on which airborne particles are collected, e.g. a filter or a polyurethane foam
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3.3.2
inhalable sampler
sampler which collects the inhalable fraction of airborne particles
3.3.3
particle/vapour mixture
aerosol consisting of airborne particles and vapour
[ENV 13936 [3]]
3.3.4
respirable sampler
sampler which collects the respirable fraction of airborne particles
3.3.5
sample
collection substrate and the airborne particles collected on it, including, if appropriate, airborne particles collected
on the internal surfaces of the sampler
3.3.6
sampler
device for collecting airborne particles
3.4 Statistical terms
3.4.1
analytical bias
bias of the analytical method
3.4.2
analytical precision
imprecision arising from analytical variability
3.4.3
analytical recovery
ratio of the mass of analyte measured in a sample to the known mass of analyte in that sample, expressed as a
percentage
3.4.4
detection limit
lowest concentration of an analyte that the analytical process can reliably detect
3.4.5
quantification limit
lowest concentration of an analyte that the analytical process can report with a specified degree of certainty
3.4.6
sampler bias
bias of the sampling method
3.4.7
sampling precision
combination of the imprecision of the aerosol sampling process and the imprecision arising from the flow rate
variability
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4 Principle
Sampler bias and sampling precision are estimated by examining sampler performance data reported in the
scientific literature.
For measuring procedures that specify a method for the determination of soluble metals and metalloids, the
analytical bias is, by definition, taken to be zero.
For measuring procedures that specify a method for the determination of total metals and metalloids that involves
sample dissolution, the analytical bias is determined by assessing the effectiveness of the sample dissolution
method described in the procedure. This is achieved by analysing reference samples, which can be pure
compounds, bulk reference materials and/or samples of dust on collection substrates, and determining the
analytical recovery of the metals and metalloids of interest. The analytical recovery is then carefully scrutinised to
determine a typical upper limit for the analytical bias.
For measuring procedures that do not involve sample dissolution, e.g. X-ray fluorescence spectrometry, the
analytical bias is determined by comparison with a reference method or by analysis of a reference material.
Alternatively, in some instances, it can be estimated theoretically.
For measuring procedures that involve sample dissolution, the analytical precision is determined by analysing
reference samples prepared by spiking collection substrates with standard solutions of the metals and metalloids of
interest. The repeatability of measurements made on collection substrates spiked with various sample loadings
(corresponding to different concentrations of metal or metalloid in air and air sample volumes) gives a measure of
the precision of the analytical method for different averaging times across the measuring ranges specified in
EN 482.
For measuring procedures that do not involve sample dissolution, the analytical precision is determined in a similar
manner, by analysing reference samples prepared by loading collection substrates with known amounts of dust.
Alternatively, in some instances, it can be estimated theoretically.
The determined analytical bias and analytical precision are combined with the estimated sampler bias and
sampling precision to estimate the overall uncertainty of the measuring procedure as a whole. This is then
assessed against the general performance requirements prescribed in EN 482.
5 Requirements
5.1 General requirements
5.1.1 Scope of the measuring procedure
The scope of the measuring procedure shall give information about the following:
the metals and metalloids that are covered by the measuring procedure, and the analytical techniques used;
the working range;
metal and metalloid compounds and/or dusts that could be found in workplace air, for which the sample
preparation method described is known to be inadequate;
any known interferences.
5.1.2 Method performance
The measuring procedure shall give information about method performance, including the following:
metal and metalloid compounds and/or dusts for which the sample preparation method described has been
shown to be effective;
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the range of concentrations of metals and metalloids in air and sample volumes over which the measurement
method has been shown to meet the acceptance criteria for overall uncertainty prescribed in EN 482;
the detection limits and quantification limits of the analytical method for the metals and metalloids of interest;
full details of any known interferences, including suitable and sufficient information on how to minimise their
effects.
5.1.3 Safety information
The measuring procedure shall provide suitable and sufficient information on the safety hazards associated with
the reagents and equipment used in the procedure.
5.1.4 Samplers
The measuring procedure shall:
require the user to select samplers that are designed to collect an appropriate fraction of airborne particles, as
defined in EN 481, according to the particle size fraction(s) that is applicable to the exposure limits for the
metals and metalloids of interest (for example, an inhalable sampler or a respirable sampler can be used);
specify that the samplers shall comply with the provisions of EN 13205.
5.1.5 Sampling pumps
The measuring procedure shall require the user to use sampling pumps that comply with the provisions of EN 1232
or EN 12919.
5.1.6 Quantification limit
When tested in accordance with 9.1, the quantification limit shall be lower than the mass of metal or metalloid that
would be sampled at 0,1 times the limit value for the minimum air sample volume specified in the measuring
procedure.
5.1.7 Other detailed requirements
Where necessary, the measuring procedure shall give other detailed requirements, e.g. for the collection substrate.
5.2 Analytical recovery
When tested in accordance with 9.3.2 the upper limit of the 95 % confidence interval of the mean analytical
recovery shall be at least 90 % for all test materials.
5.3 Overall uncertainty
The overall uncertainty shall conform with the requirements specified in Table 1 of EN 482:1994.
6 Reagents
During the analysis, use only reagents of analytical grade, and only water complying with the requirements for
EN ISO 3696 grade 2 water (electrical conductivity less than 0,1 mS/m and resistivity greater than 0,01 MW
25 °C).
NOTE It is recommended that the water used be obtained from a water purification system that delivers ultrapure water
having a resistivity greater than 0,18 MW
MW
water).
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7 Reference samples
7.1 Standard solutions
Standard solutions with concentrations of the metals and metalloids of interest that are traceable to National and/or
International Standards. If commercial standard solutions are used observe the manufacturer's expiry date or
recommended shelf life.
7.2 Reference materials
For each metal or metalloid, a range of reference materials that is representative of the substances of interest that
could be present in the workplace atmosphere. The reference materials can be pure compounds of known
composition, certified reference materials or other well characterised materials (e.g. materials characterised in an
interlaboratory comparison). Follow the supplier's instructions when using certified reference materials.
NOTE 1 If there is a limit value for a specific compound, that compound should be included in the range of reference
materials.
NOTE 2 For a method that is intended to have general applicability, the range of reference materials should include
compounds and materials in industrial use and compounds and materials which could be generated by the work activity.
NOTE 3 It is important that the particle size of the reference materials be as close as possible to that of the particles
analysed, since inhalable particles are small and often much more easily soluble than coarse bulk materials.
7.3 Reference air samples
Samples of dust on collection substrates (e.g. airborne particles collected on filters using a multiple simultaneous
sample collection system), having a known or measured loading of the metals and metalloids of interest.
8 Apparatus
Usual laboratory apparatus and resources and:
a system for applying a known volume of standard solution to the collection substrate with a precision of better
than 1 %;
an instrument or instruments for analysing the metals and metalloids of interest.
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9 Test methods
9.1 Detection limits and quantification limits
9.1.1 Determination of detection limits and quantification limits
9.1.1.1 Prepare and analyse 10 unused collection substrates, as described in the measuring procedure.
Calculate the mean and standard deviation of the measured concentrations for each analyte. Multiply the standard
deviations by three to obtain the detection limits and by ten to obtain the quantification limits.
9.1.1.2 If there is no measurable response from the analytical instrument when the blanks are analysed, spike
10 unused collection substrates with an appropriate mass of analyte, such that the test solutions/suspensions
produced from them will have a concentration near the anticipated detection limit, and repeat the test described
in 9.1.1.1.
9.1.2 Comparison of results with the acceptance criteria
Compare the quantification limits obtained in 9.1.1 with the requirements of 5.1.6.
9.2 Selection of test methods for determination of analytical bias and precision
Different test methods are applicable for determination of analytical bias and precision, depending on the sample
preparation method used. Refer to annex A for guidance on which of the test methods described in this standard
are applicable for the measuring procedure to be evaluated.
9.3 Analytical bias
9.3.1 Consideration of the analytical bias of procedures for soluble metals and metalloids
Soluble compounds of metals and metalloids are defined by the specific leach solution and leach conditions used
in the measuring procedure prescribed for their determination when the limit value is set. This is because, except
for compounds that are very soluble or very insoluble in water, solubility can be dependent upon the nature of the
leach solution and parameters such as particle size, solute/solvent ratio, temperature etc. Consequently, the
sample dissolution method, by definition, gives appropriate results, and there is no analytical bias.
NOTE 1 Although the sample dissolution methods for soluble compounds are generally design-based, there are
circumstances in which they can give incorrect results. In particular, this can occur if a soluble compound reacts with the filter
material, or a contaminant on a filter, to produce an insoluble compound. For example, a low recovery will be obtained for
soluble silver compounds if the filter used is contaminated with chloride. It is therefore important that proper consideration is
given to chemical compatibility when selecting a filter for collecting samples of soluble compounds (see annex A of
IS
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