SIST EN 15051-1:2026
(Main)Workplace exposure - Measurement of the dustiness of bulk materials - Part 1: Requirements and choice of test methods
Workplace exposure - Measurement of the dustiness of bulk materials - Part 1: Requirements and choice of test methods
This document specifies the environmental conditions, the sample handling and analytical procedures and the method of calculating and presenting the results. Reasons are given for the need for more than one method and advice is given on the choice of method to be used.
This document establishes a categorization scheme for dustiness to provide a standardized way to express and communicate the results to users of the bulk materials. Details of the scheme for each method are given in FprEN 15051-2:2025 and FprEN 15051-3:2025.
This document is applicable to powdered, granular or pelletized bulk materials.
This document does not apply to test the dust released during mechanical reduction of solid bulk materials (e.g. cut, crushed) or to test application procedures for the bulk materials.
Exposition am Arbeitsplatz Messung des Staubungsverhaltens von Schüttgütern - Teil 1: Anforderungen und Auswahl der Prüfverfahren
Dieses Dokument legt die Umgebungsbedingungen, das Verfahren zur Handhabung der Proben und das Verfahren zur Berechnung und Darstellung der Ergebnisse fest. Es wird begründet, warum mehr als ein Verfahren benötigt wird, und es wird Hilfestellung bei der Auswahl des zu verwendenden Verfahrens gegeben.
Dieses Dokument stellt ein Kategorisierungssystem für das Staubungsverhalten auf, um eine genormte Grundlage für die Angabe und Weiterleitung der Ergebnisse an die Anwender von Schüttgütern zu schaffen. Einzelheiten zu dem System für die einzelnen Verfahren sind in EN 15051 2:2025 und EN 15051 3:2025 enthalten.
Dieses Dokument ist anwendbar für pulverförmige, granulierte oder pelletierte Schüttgüter.
Dieses Dokument ist weder für die Prüfung von Staub, der bei der mechanischen Zerkleinerung fester Schüttgüter (z. B. beim Schneiden, Brechen) freigesetzt wird, noch für die Prüfung der Anwendungsverfahren von Schüttgütern anwendbar.
Exposition sur les lieux de travail - Mesurage du pouvoir de resuspension des matériaux pulvérulents en vrac - Partie 2 : Méthode du tambour rotatif
Le présent document spécifie également les conditions ambiantes, les méthodes de manipulation et d’analyse des échantillons ainsi que la méthode de calcul et d’expression des résultats. Le besoin de disposer de plusieurs méthodes est justifié et des conseils sont donnés sur la sélection de la méthode.
Le présent document établit un schéma de classification du pouvoir de resuspension afin de fournir une méthode normalisée pour exprimer et communiquer les résultats aux utilisateurs de matériaux en vrac. Des détails concernant cette classification sont donnés, pour chaque méthode, dans l’EN 15051-2:2025 et l’EN 15051-3:2025.
Le présent document s’applique aux matériaux en vrac granulaires, en poudre ou sous forme de pastilles.
Le présent document ne s’applique pas à la détermination de l’empoussièrement dû à la réduction mécanique (par exemple découpe, concassage) de matériaux solides en vrac ni à l’évaluation des méthodes d’application des matériaux en vrac.
Izpostavljenost na delovnem mestu - Meritve prašnosti razsutih materialov - 1. del: Zahteve in izbira preskusnih metod
General Information
Relations
Standards Content (Sample)
SLOVENSKI STANDARD
oSIST prEN 15051-1:2024
01-julij-2024
Izpostavljenost na delovnem mestu - Meritve prašnosti razsutih materialov - 1. del:
Zahteve in izbira preskusnih metod
Workplace exposure - Measurement of the dustiness of bulk materials - Part 1:
Requirements and choice of test methods
Exposition am Arbeitsplatz Messung des Staubungsverhaltens von Schüttgütern - Teil 1:
Anforderungen und Auswahl der Prüfverfahren
Exposition sur les lieux de travail - Mesurage du pouvoir de resuspension des matériaux
pulvérulents en vrac - Partie 2 : Méthode du tambour rotatif
Ta slovenski standard je istoveten z: prEN 15051-1
ICS:
13.040.30 Kakovost zraka na delovnem Workplace atmospheres
mestu
oSIST prEN 15051-1:2024 en,fr,de
2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.
oSIST prEN 15051-1:2024
oSIST prEN 15051-1:2024
DRAFT
EUROPEAN STANDARD
prEN 15051-1
NORME EUROPÉENNE
EUROPÄISCHE NORM
June 2024
ICS 13.040.30 Will supersede EN 15051-1:2013
English Version
Workplace exposure - Measurement of the dustiness of
bulk materials - Part 1: Requirements and choice of test
methods
Exposition sur les lieux de travail - Mesurage du Exposition am Arbeitsplatz Messung des
pouvoir de resuspension des matériaux pulvérulents Staubungsverhaltens von Schüttgütern - Teil 1:
en vrac - Partie 2 : Méthode du tambour rotatif Anforderungen und Auswahl der Prüfverfahren
This draft European Standard is submitted to CEN members for enquiry. It has been drawn up by the Technical Committee
CEN/TC 137.
If this draft becomes a European Standard, 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.
This draft European Standard was established by CEN 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 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, France, Germany, Greece, Hungary, Iceland, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta, Netherlands, Norway,
Poland, Portugal, Republic of North Macedonia, Romania, Serbia, Slovakia, Slovenia, Spain, Sweden, Switzerland, Türkiye and
United Kingdom.
Recipients of this draft are invited to submit, with their comments, notification of any relevant patent rights of which they are
aware and to provide supporting documentation.
Warning : This document is not a European Standard. It is distributed for review and comments. It is subject to change without
notice and shall not be referred to as a European Standard.
EUROPEAN COMMITTEE FOR STANDARDIZATION
COMITÉ EUROPÉEN DE NORMALISATION
EUROPÄISCHES KOMITEE FÜR NORMUNG
CEN-CENELEC Management Centre: Rue de la Science 23, B-1040 Brussels
© 2024 CEN All rights of exploitation in any form and by any means reserved Ref. No. prEN 15051-1:2024 E
worldwide for CEN national Members.
oSIST prEN 15051-1:2024
prEN 15051-1:2024 (E)
Contents Page
European foreword . 3
Introduction . 4
1 Scope . 6
2 Normative references . 6
3 Terms and definitions . 6
4 Principles . 7
5 General Procedures . 7
5.1 Schematic overview of the procedure . 7
5.2 Conditioning of the bulk material . 9
5.2.1 As-received condition. 9
5.2.2 Conditioning specifications . 9
5.3 Sample and environmental control . 9
5.4 Taking samples from the bulk material . 9
5.5 Moisture content . 10
5.6 Bulk density . 10
5.7 Test procedure . 10
5.8 Replicate tests . 10
5.9 In-house / test powder . 10
5.10 Reporting . 10
6 Choice of test methods . 10
6.1 General. 10
6.2 Selection of the most appropriate test method. 11
7 Evaluation of dustiness . 11
8 Test report . 12
Annex A (normative) Determination of moisture content . 13
Annex B (normative) Determination of bulk density of the test material . 15
Annex C (informative) Spheriglass 5000 CP00 – An example of a suitable powder for quality
purposes . 16
Bibliography . 17
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prEN 15051-1:2024 (E)
European foreword
This document (prEN 15051-1:2024) has been prepared by Technical Committee CEN/TC 137
“Assessment of workplace exposure to chemical and biological agents”, the secretariat of which is held
by DIN.
This document is currently submitted to the CEN Enquiry.
This document will supersede EN 15051-1:2013.
prEN 15051-1:2024 includes the following significant technical changes with respect to
EN 15051-1:2013:
— The introduction was revised to better explain the purpose of dustiness testing;
— Clause 5.1: a schematic overview of the test procedure has been added;
— Clause 5.8: information about an in-house / test powder has been added;
— Annex C: an example of a suitable powder for quality purposes (Spheriglass 5000 CP00) has been
added.
EN 15051 Workplace exposure – Measurement of the dustiness of bulk materials consists of the following
parts:
— Part 1: Requirements and choice of test methods;
— Part 2: Rotating drum method;
— Part 3: Continuous drop method.
EN 15051-2 and EN 15051-3 give details of two test apparatus and test methods for the reproducible
production of dust from a bulk material under standard conditions, and the measurement of the
inhalable, thoracic and respirable fractions of this dust, with reference to the existing European
Standards, where relevant (see Clause 6).
oSIST prEN 15051-1:2024
prEN 15051-1:2024 (E)
Introduction
The control of dust emissions during the handling and transportation of bulk materials is an important
consideration in the design and operation of many industrial processes. Excessive airborne dust levels in
workplaces are undesirable for several reasons:
— they can cause adverse health effects to the workers;
— their control can involve the use of costly ventilation and filtration systems;
— they can contaminate machinery and products;
— they can be costly in terms of product losses.
It is therefore advantageous for occupational hygienists and process engineers to have relevant
information about the propensity of bulk materials to release airborne particles (i.e. dust) (the
“dustiness” of the bulk material) so that risks can be evaluated, controlled and minimized.
Dustiness testing measures the propensity of a bulk materials e.g. powder to become airborne in response
to a mechanical stimulus. Dustiness is a relative term and the measurement obtained will depend on
defined method parameters including: the test apparatus used (design and volume), the mechanical
stimulus and energy level applied, the condition and properties of the tested bulk material, the amount
of bulk material tested (volume or mass), the sampling duration or volume of air sampled and various
environmental variables (e.g. relative humidity, temperature and electrostatic effects). If one changes the
extent of one or more method parameters then the outcome (e.g. dustiness values) can change
significantly. The test and the variables therefore need to be closely specified to ensure reproducibility.
A single method of dustiness testing is unlikely to represent and reproduce the many types of processing
and handling used in industry. This has meant that a number of bespoke methods have been developed
and used in some industry sectors but are limited in their scope and application and were not designed
to measure and express results in terms of the health-related fractions: i.e. inhalable, thoracic and
respirable, as defined in EN 481. Therefore, a clear need for a standard was presented and EN 15051-1
was published in 2013. The standard series included two test methods; EN 15051-2 (rotating drum test)
and EN 15051-3 (continuous drop test), to simulate two of the main handling methods: small-scale
repeated discreet handling (e.g. shovelling, dispensing, batch preparation and weighing etc.) and larger
scale conveyancing of bulk dust into silos and hoppers. EN 15051-2 separates the airborne dust into the
three health related fractions using porous foams and EN 15051-3 measures the respirable fraction using
a well-characterized cyclone sampler.
This document was originally developed based on the results of the European project SMT4-CT96-
2074 Development of a Method for Dustiness Testing (see [1]). This project investigated the dustiness of
12 bulk materials, with the intention to test as wide a range of bulk materials as possible, i.e. magnitude
of dustiness, industrial sectors, chemical composition and particle size distribution. The first revision
considered important comments from industrial users of the standard (e.g. Industrial Minerals
Association), a number of research papers (for example, [2] and [3]) and the potential influence of the
expanding database of dustiness results. In this revised version, the performance and characteristics of
the metal foams for the sampling of the respirable fraction and important comments from industrial users
of the standard have been taken into account.
The level of the dustiness generally depends on material-specific and process-specific parameters. The
most important material-specific parameters are:
— the particle size distribution of the bulk material;
— its bulk density;
oSIST prEN 15051-1:2024
prEN 15051-1:2024 (E)
— its moisture content (“bulk material moisture content”);
— its chemical composition;
— physical characteristics like electrostatic charge distribution.
Process-specific parameters are mainly determined by the type of handling and are essentially
determined by:
— the type and level of energy that leads to dust release;
— the duration of the energy effect.
For a specific chemical substance in a powder form, it is important to understand that its particle size
distribution cannot predict its dustiness behaviour and respectively its dustiness values cannot predict
the size distribution of this substance.
The format and calculation of the dustiness test results are expressed in terms of the ratio of the mass of
dust released of specific health-related fractions (mg) / mass of material tested (kg) for defined method
parameters. They are relative values, so a specific scale for dustiness has been derived for each method,
which enables a categorization of the powder into: very low, low, medium and high dustiness categories,
for the applicable health-related fraction/s measured. The scale is specific to the dustiness method
selected and for the defined method parameters.
The dustiness values of a specific method can be used for comparing and ranking powders and assess
whether the current controls are adequate. The information also supports risk and safe by design
assessments. The results provide users (e.g. manufacturers, producers, occupational hygienists and
workers) with information on the potential for dust emissions, when the bulk material is handled or
processed in workplaces. It provides the manufacturers of bulk materials with information that can help
to improve their products. It allows the users of the bulk materials to assess the effects of pre-treatments,
and also to select less dusty products, if available. It is envisaged that different branches of industry might
develop their own categorization schemes using experimentally determined dustiness values of the bulk
materials of interest.
However, dustiness test methods measure dust at source emission and does not consider the
transportation of the airborne particles within a workplace environment to the breathing zone of a
worker. Concentrations of respirable, thoracic or inhalable dust in the workplace air, resulting from the
processing and handling of bulk materials, will depend on a wide variety of factors (e.g. environmental
factors, quantity used, engineering controls, transport of particles from source to worker’s breathing
zone, type of activities). Therefore, dustiness values do not provide workplace exposure concentrations.
The test methods produce samples with the potential for chemical analysis of the contents. However, it
is important to understand that for a mixture, the mass percentage of a substance in the bulk material
will be different (lower or higher) to the mass percentage of the same substance in the dust collected by
the foams and the filter (rotating drum) or by the respirable and inhalable samplers (continuous drop).
A bulk material is expected to be made of solid particles and granular materials. For a mixture, the size
distribution of each substance is likely to be different and furthermore, during disturbance and attrition
of the bulk material in the dustiness testers, it is very likely that the airborne particle size distribution of
each substance is different from each other and from its original size distribution in the bulk material.
This document does not discuss the sample preparation for further chemical analysis of dust released
from bulk materials (except in terms of health-related fractions).
For the measurement of dustiness of bulk materials that possibly contain or release nano-objects and
their agglomerates and aggregates(NOAA), the reader should consult the EN 17199 series [4, 5, 6, 7, 8].
oSIST prEN 15051-1:2024
prEN 15051-1:2024 (E)
1 Scope
This document specifies the environmental conditions, the sample handling and analytical procedures
and the method of calculating and presenting the results. Reasons are given for the need for more than
one method and advice is given on the choice of method to be used.
This document establishes a categorization scheme for dustiness to provide a standardized way to
express and communicate the results to users of the bulk materials. Details of the scheme for each method
are given in EN 15051-2 and EN 15051-3.
This document is applicable to powdered, granular or pelletized bulk materials.
This document is not applicable to test the dust released during mechanical reduction of solid bulk
materials (e.g. cut, crushed) or to test application procedures for the bulk materials.
2 Normative references
The following documents are referred to in the text in such a way that some or all of their content
constitutes requirements 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.
EN 1540, Workplace exposure — Terminology
EN 15051-2, Workplace exposure — Measurement of the dustiness of bulk materials — Part 2: Rotating
drum method
EN 15051-3, Workplace exposure — Measurement of the dustiness of bulk materials — Part 3: Continuous
drop method
3 Terms and definitions
For the purpose of this document, the terms and definitions given in EN 1540 and the following apply.
NOTE In particular, the following terms of EN 1540 are used in this document: airborne dust, dustiness,
dustiness mass fraction, inhalable fraction, respirable fraction, thoracic fraction and health related fractions.
ISO and IEC maintain terminology databases for use in standardization at the following addresses:
— ISO Online browsing platform: available at https://www.iso.org/obp/
— IEC Electropedia: available at https://www.electropedia.org/
3.1
inhalable dustiness mass fraction
w
I,t
ratio of the inhalable dust produced by the dustiness test procedure, to the test mass for the respective
test method t
Note 1 to entry: The different test methods are described in EN 15051-2 and EN 15051-3, and t has the value A and
B for the two methods respectively.
3.2
respirable dustiness mass fraction
w
R,t
ratio of the respirable dust produced by the dustiness test procedure to the test mass for the respective
test method t
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prEN 15051-1:2024 (E)
Note 1 to entry: The different test methods are described in EN 15051-2 and EN 15051-3, and t has the value A and
B for the two methods respectively.
3.3
thoracic dustiness mass fraction
w
T,t
ratio of the thoracic dust produced by the dustiness test procedure to the initial mass for the respective
test method t
Note 1 to entry: The different test methods are described in EN 15051-2 and EN 15051-3, and t has the value A and
B for the two methods respectively.
4 Principles
A dustiness tester consists of the following elements:
— dust generation section;
— dust transfer section;
— sampling section;
— size fractionator(s);
— dust collection section.
A standard volume or a minimum quantity of bulk material, with known moisture content and bulk
density, is weighed and then placed in the dust generation section, where it is treated under standard
conditions for a set period of time. The airborne dust released is drawn from the dust generation section,
through the dust transfer section, into the sampling section. Here, the size fractionator(s) classifies the
airborne dust according to aerodynamic particle size. The dust collection section deposits the dust
fractions onto suitable media for gravimetric analysis. The results are used to calculate the inhalable,
thoracic and respirable dustiness mass fractions of the released dust, in relation to the initial mass of bulk
material used. These dat
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