SIST EN 15002:2006
(Main)Characterization of waste - Preparation of test portions from the laboratory sample
Characterization of waste - Preparation of test portions from the laboratory sample
This European Standard is applicable for the preparation of representative test portions from the laboratory sample that has been taken according to the sampling plan (EN 14899), prior to physical and/or chemical analysis (e.g. preparation of eluates, extractions, digestion and/or analytical determinations) of solid and liquid samples and sludge. It is also applicable for the preparation of test portions from digests and eluates for the subsequent analyses.
This European Standard is intended to find the correct sequence of operations and treatments to be applied to the laboratory sample in order to obtain suitable test portions in compliance with the specific requirements defined in the corresponding analytical procedures.
Charakterisierung von Abfällen - Herstellung von Prüfmengen aus der Laboratoriumsprobe
Diese Europäische Norm ist anwendbar bei der Aufbereitung von repräsentativen Prüfmengen aus der Laboratoriumsprobe, die nach dem Probenahmeplan (prEN 14899) entnommen wurde, vor der physikalischen und/oder chemischen Analyse (z. B. Herstellung von Eluaten, Extraktionen, Aufschlüsse und/oder analytische Bestimmungen) von festen und flüssigen Proben sowie von Schlamm. Sie gilt auch für die Vorbereitung von Prüfmengen aus Aufschlüssen und Eluaten für die anschließende Analyse.
Diese Europäische Norm ist dafür vorgesehen, die richtige Reihenfolge von Arbeitsschritten und Behandlungen herauszufinden, die auf die Laboratoriumsproben anzuwenden sind, um geeignete Prüfmengen unter Beachtung der in den entsprechenden Analysenverfahren festgelegten spezifischen Anforderungen zu erhalten.
Caractérisation des déchets - Préparation de prises d'essai a partir de l'échantillon pour laboratoire
Karakterizacija odpadkov – Priprava preskusnih vzorcev iz laboratorijskega vzorca
General Information
Relations
Standards Content (Sample)
SLOVENSKI STANDARD
SIST EN 15002:2006
01-maj-2006
Karakterizacija odpadkov – Priprava preskusnih vzorcev iz laboratorijskega vzorca
Characterization of waste - Preparation of test portions from the laboratory sample
Charakterisierung von Abfällen - Herstellung von Prüfmengen aus der
Laboratoriumsprobe
Caractérisation des déchets - Préparation de prises d'essai a partir de l'échantillon pour
laboratoire
Ta slovenski standard je istoveten z: EN 15002:2006
ICS:
13.030.01 Odpadki na splošno Wastes in general
SIST EN 15002:2006 en,fr,de
2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.
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SIST EN 15002:2006
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SIST EN 15002:2006
EUROPEAN STANDARD
EN 15002
NORME EUROPÉENNE
EUROPÄISCHE NORM
February 2006
ICS 13.030.01
English Version
Characterization of waste - Preparation of test portions from the
laboratory sample
Caractérisation des déchets - Préparation de prises d'essai Charakterisierung von Abfällen - Herstellung von
à partir de l'échantillon pour laboratoire Prüfmengen aus der Laboratoriumsprobe
This European Standard was approved by CEN on 30 December 2005.
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, Romania,
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
© 2006 CEN All rights of exploitation in any form and by any means reserved Ref. No. EN 15002:2006: E
worldwide for CEN national Members.
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EN 15002:2006 (E)
Contents Page
Foreword .3
Introduction.4
1 Scope .5
2 Normative references .6
3 Terms and definitions.6
4 Equipment .8
5 Interferences and sources of error.8
6 Procedure .8
6.1 Key concepts.8
6.2 Sequence of treatment techniques.10
7 Report .12
Annex A (normative) Guideline for choosing sample treatment techniques .13
Annex B (informative) Relationship between minimum amount of (sub-)sample and particle size.27
Annex C (informative) Sample treatment equipment.30
Annex D (informative) Examples for analytical methods .31
Annex E (informative) Examples for preparation of test samples .37
Bibliography.49
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Foreword
This European Standard (EN 15002:2006) has been prepared by Technical Committee CEN/TC 292
“Characterisation of waste”, the secretariat of which is held by NEN.
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 August 2006, and conflicting national standards shall be withdrawn at
the latest by August 2006.
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, Romania, Slovakia, Slovenia, Spain, Sweden,
Switzerland and United Kingdom.
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Introduction
In laboratory praxis, very often different analytical procedures have to be applied to the laboratory sample that
has been taken according to the sampling plan. For this purpose subsampling has to be applied in a way, that
the different test portions are representative for the original laboratory sample with respect to the compounds
of interest and the specific analytical procedures. The representativity of the laboratory sample and of the test
portions is of major importance to guarantee the quality and accuracy of analytical results. The representativity
of the laboratory sample is specified by the sampling plan. This European Standard specifies the correct
sequence of operations to ensure the representativity of the test portions.
Safety remarks
Anyone dealing with waste and sludge analysis has to be aware of the typical risks of that kind of material
irrespective of the parameter to be determined. Waste and sludge samples may contain hazardous (e.g. toxic,
reactive, flammable and infectious) substances, which can be liable to biological and/or chemical reaction.
Consequently it is recommended that these samples should be handled with special care. The gases that may
be produced by microbiological or chemical activity are potentially flammable and will pressurise sealed
bottles. Bursting bottles are likely to result in hazardous shrapnel, dust and/or aerosol. National regulations
should be followed with respect to all hazards associated with this method.
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1 Scope
This European Standard is applicable for the preparation of representative test portions from the laboratory
sample that has been taken according to the sampling plan (EN 14899), prior to physical and/or chemical
analysis (e.g. preparation of eluates, extractions, digestion and/or analytical determinations) of solid and liquid
samples and sludge. It is also applicable for the preparation of test portions from digests and eluates for the
subsequent analyses.
This European Standard is intended to find the correct sequence of operations and treatments to be applied to
the laboratory sample in order to obtain suitable test portions in compliance with the specific requirements
defined in the corresponding analytical procedures.
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2 Normative references
The following referenced documents are indispensable for the application of this European Standard. For
dated references, only the edition cited applies. For undated references, the latest edition of the referenced
document (including any amendments) applies.
ISO 11465:1993, Soil quality – Determination of dry matter and water content on a mass basis – Gravimetric
method
ISO 14507:2003, Soil quality — Pretreatment of samples for determination of organic contaminants
3 Terms and definitions
For the purposes of this European Standard, the following terms and definitions apply.
3.1
sample
portion of material selected from a larger quantity of material
3.2
laboratory sample
sample sent to or received by the laboratory
NOTE 1 When the laboratory sample is further prepared (reduced) by subdividing, mixing, grinding, or by combinations
of these operations, the result is the test sample. When no preparation of the laboratory sample is required, the laboratory
sample is the test sample. A test portion is removed from the test sample for the performance of the test or for analysis.
NOTE 2 The laboratory sample is the final sample from the point of view of sample collection but it is the initial sample
from the point of view of the laboratory.
NOTE 3 Several laboratory samples may be prepared and sent to different laboratories or to the same laboratory for
different purposes. When sent to the same laboratory, the set is generally considered as a single laboratory sample and is
documented as a single sample.
3.3
test sample; analytical sample
sample, prepared from the laboratory sample, from which test portions are removed for testing or analysis
3.4
test portion; analytical portion
quantity of material of proper size, for measurement of the concentration or other properties of interest,
removed from the test sample
NOTE The test portion may be taken from the laboratory sample directly if no preparation of sample is required (e. g.
with liquids or samples of proper homogeneity, size and fineness), but usually it is taken from the prepared test sample.
3.5
sub-sample
sample obtained by procedures in which the items of interest are randomly distributed in parts of equal or
unequal size
NOTE A sub-sample may be:
a) portion of the sample obtained by selection or division;
b) the final sample of multistage sample-preparation.
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3.6
fraction
sample obtained by procedures from the laboratory sample where the properties of interest may be unequally
distributed
NOTE A fraction may consist of metal pieces, stones etc.
3.7
volatile organic compounds
organic compound having a boiling point below 300 °C (at a pressure of 101 kPa)
NOTE This includes volatile aromatic and volatile halogenated hydrocarbons as determined in accordance with
ISO 15009. Some mono- and dichlorophenols, for instance, and naphthalene also belong to this group.
3.8
moderately volatile organic compounds
organic compound having a boiling point above 300 °C (at a pressure of 101 kPa)
NOTE This definition includes:
a) mineral oil;
b) most polycyclic aromatic hydrocarbons (PAH) (see ISO 13877);
c) polychlorobiphenyls (PCB) (see ISO 10382);
d) organochlorine pesticides (see ISO 10382).
3.9
moderately volatile compounds
sum of moderately volatile organic compounds and volatile inorganic compounds (e.g. mercury, arsenic
cadmium, thallium) that can be lost during sample preparation (e.g. heating)
3.10
homogenisation
process of combining of components, particles or layers into a more homogeneous state of the original
samples (in the case of composite samples) or pre-treated fractions of samples in order to ensure equal
distribution of substances in and properties of the sample
3.11
phase separation; fraction separation
process of dividing components, particles or layers if homogenisation of the sample is practically not
applicable and/or the analysis of different fractions or phases are appropriate
3.12
drying
process of removing water from a sample
NOTE For the purpose of test portion preparation, it may be useful to remove just the amount of water that could
interfere with other processes involved (e.g. during crushing or milling). In order to minimise the alteration of the sample
during test portion preparation, removing the total amount of water present in the sample is not necessarily needed.
3.13
particle size reduction
mechanical friction of the sample by milling, grinding, crushing or cutting
3.14
sub-sampling
process of selecting one or more sub-samples from a sample
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4 Equipment
For the purpose of preparation of test portions from the laboratory samples appropriate equipment has to be
chosen depending on the procedures selected according to Annex A.
In the selection of the type of treatment techniques, one should keep in mind that each of them has some
potential impact on analytical results, because it can introduce contamination or alter the physical-chemical
properties of the sample.
All glassware and devices that come in contact with the sample shall be made out of a suitable material,
chemically compatible with the sample, selected in order to minimize contamination of samples (e.g. plastic
materials for inorganic elemental analysis, quartz or glass for volatile and organic analytes). Care shall be
taken to ensure a good cleaning, in order to avoid cross-contamination of samples.
An informative list of appropriate equipment for the sample treatment procedures is given in Annex C.
5 Interferences and sources of error
The (sub)-sample shall be re-homogenised after any operation that may have resulted in segregation of
different sized particles.
Care should be taken to avoid loss of material and contamination of the sample via the air, by dust, by the use
of the apparatus (e.g. from the ambient laboratory atmosphere or between samples stored or processed close
to one another).
Three types of contamination could occur from the apparatus:
abrasion;
cross-contamination;
chemical release.
It is recommended to perform treatment of waste material in a separate room used only for this purpose,
especially crushing or sieving.
If the sample has a dust-like consistency or contains (semi)-volatile compounds, part of it may be lost and this
may alter its physical-chemical properties.
6 Procedure
6.1 Key concepts
Preparation of the test portion can be a complex process, because of a number of factors: sample type and its
physical state, amount of laboratory sample, type and number of determinations to be carried out etc. The
prepared test portions shall satisfy the following requirements at the same time:
each test portion shall be as representative as possible of the laboratory sample;
the amount and the physical state (e.g. particle size) of each test portion have to comply with the
requirements of the respective analytical technique;
for each test portion, no losses of and no contamination with respective analytes of interest should
occur.
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The preparation of the test portions from the laboratory sample, that has been taken according to the sampling
plan, is related to the requested analytical determinations. This means that, if needed, contact has to be
established among all involved parties such as the sampler, the customer and the analytical laboratory to
achieve the requirements of the standards to be used for the requested determinations.
The preparation of test portions in the laboratory will frequently involve a sequence of operations such as
homogenisation, phase separation, drying, reducing particle size and sub sampling. Specific forms of these
operations are described in A.2 to A.6, respectively. A number of decisions on the specific order of these
operations for a particular laboratory sample have to be made. In some cases, the sequence of operations to
be applied is rather straightforward, but in more complicated cases (e.g. when several determinations with
different requirements have to be performed) it can be critical to choose the right sequence of such operations.
For soil samples more specific procedures are described in ISO 11464 for inorganic parameters or in ISO
14507 for organic parameters.
In order to define the operations to be applied to a laboratory sample to produce one or more representative
test portions, three main steps have to be considered:
Definition of analytical requirements
First, the requirements of analytical procedures of interest shall be defined:
what methods shall be used;
how many test portions are necessary;
quantity and properties of the test portions necessary for each analytical procedure;
preservation requirements (e.g. time frame, temperature, addition of reagents).
NOTE 1 Indicative amounts of test portions and specific requirements of the analytical methods involved are
given in Annex D. It is recommended to prepare at least five times the amounts needed as test portions for the
tests.
Definition of sequence of operations
Then, the sequence of operations shall be defined according to the flow sheet (Figure 1), based on
the properties of the laboratory sample and the requirements of the analytical procedures: each
single operation of this sequence has to be considered like an independent module; available
modules are:
phase/fraction separation;
drying;
particle size reduction;
homogenisation;
sub-sampling.
NOTE 2 For practical reasons it is recommended to group the parameters in a way that test samples with
similar requirements can be prepared for several parameters. The same test sample may be used for different
parameters if it fulfils the necessary requirements.
Frequently, different determinations have to be performed on the laboratory samples. In those cases,
modules have to be combined and/or repeated to obtain sub-samples, finally resulting in different test
portions. In order to define the actual sequence of operations to be applied to a given sample, the
flow sheet (Figure 1) shall be used.
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Choice of appropriate procedures
According to the requirements of the respective analytical techniques and the properties of the
sample the appropriate sample treatment technique has to be chosen within each module by
following the instructions of Annex A. Instructions are given in this annex in which case a particular
operation is appropriate to use.
6.2 Sequence of treatment techniques
The flow sheet in Figure 1 describes the procedure to enable decisions on the specific order of treatment
operations for a particular laboratory sample in order to yield in representative test portions. It shall be applied
on the starting laboratory sample and repeated on all sample fractions or sub-samples subsequently obtained
during the preparation, in an iterative cycle until all analytical requirements are fulfilled.
If volatile compounds or moderately volatile compounds are parameters of interest this should be considered
in the sampling plan and may result in separate samples. In case of a single laboratory sample special care
has to be taken in order to avoid losses of the volatile compounds during homogenisation and/or reduction of
particle size. A preliminary sub-sampling without any homogenisation step may be necessary (see A.2.4,
A.6.4) if the representativity of the remaining sample is not substantially altered.
NOTE In special cases sub-sampling without a drying step will not lead to representative sub-samples.
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Sampling Plan
Definition of analytical
requirements
Laboratory sample,
sub-sample or sample fraction
Fractions to be further treated as
Assess required characteristics
separate sample(s); results may be
of test portion(s)
combined, if applicable
Phase/fraction
Y
Phase/fraction
separation required?
separation (A.3)
(A.3.1)
N
Y
Drying allowed and
Drying (A.4)
required? (A.4.1)
N
Particle size
Y
Particle size
reduction required and
reduction (A.5)
applicable? (A.5.1)
N
Y
Homogenisation possible?
Homogenisation (A.2)
(A.2.1)
Sub-sampling (A.6)
N
For
One or more
Y
each sub-sample:
test portions
compliance with requirements?
for analysis
N
One or more sub-samples, not yet
complying with requirements
specified in respective analytical
standards, to be further treated
Figure 1 — Flow sheet – sequence of operations
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7 Report
The work carried out by the testing laboratory shall be covered by a report which accurately, clearly and
unambiguously presents all relevant information.
Each report shall include at least the following information:
a) name, address and location of any laboratory involved in the preparation of the test portions;
b) unique identification of report (such as serial number) and of each page and total number of pages of the
report;
c) description and identification of the laboratory sample;
d) date of receipt of laboratory sample;
e) reference to this European Standard, i.e. EN 15002;
f) reference to the sampling report; if a sampling report is not available, precise reference shall be made to
the company or persons responsible for the sampling;
g) whole sequence and operating conditions (procedures and apparatuses) actually applied to the laboratory
sample for preparation of test portions;
h) any details not specified in this European Standard or which are optional, and any other factors which
may have affected the results.
For the subsequent performance of the analyses the dates of the preparation of the test portions shall be
available.
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Annex A
(normative)
Guideline for choosing sample treatment techniques
A.1 General
The preparation of test samples from a laboratory sample will frequently involve a sequence of operations
such as homogenisation, phase separation, drying, particle size reduction and sub-sampling. Specific forms of
these operations are described in this annex.
The sample treatment techniques prescribed in the analytical standards have to be fulfilled in any case.
A.2 Homogenisation
A.2.1 General information
Before each operation that implies sub-sampling, a homogenisation step is required, in order to guarantee that
all sub-samples or sample fractions have the same properties and composition. The homogenisation
technique to be used is chosen depending on the properties of the sample.
In many cases before homogenisation particle size reduction may be necessary.
If homogenisation of a sample is too difficult or even practically impossible (e.g. if the sample contains pieces
of plastic or metal), its phases shall be separated and treated as they were different samples (see A.3
phase/fraction separation).
A.2.2 Solid samples
A.2.2.1 Manual homogenisation
When to use it
Generally usable;
in cases when mechanical homogenisation could lead to loss of volatile compounds of interest.
When not to use it
For samples that form layers because of the presence of particles of different density;
for samples with particles of such a large size that homogenisation can not be reached by manual mixing.
Procedure
Mix the sample with appropriate tool (e.g. shovel, scoop, pestle and mortar). If there is a risk of losses of
volatile substances the manual homogenisation has to be done very carefully.
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A.2.2.2 Mechanical homogenisation
When to use it
Generally usable especially in cases when manual homogenisation is not suitable;
in cases of large sample sizes;
for solid samples containing particles of nearly the same density (e.g. for materials that don't form "layers"
after shaking).
When not to use it
For samples that form layers because of the presence of particles of different density; in this case, if
homogenisation is not possible separate and treat each layer as a different sample (see A.3
phase/fraction separation);
when the apparatus may heat the sample and loss of volatile analytes can occur during this process; in
this case, a manual homogenisation shall be performed.
Procedure
Operate according to the manufactures instructions.
NOTE For small sample sizes it may be also possible to use a ball-mill without balls for homogenisation.
A.2.3 Liquid samples
A.2.3.1 Manual homogenisation
When to use it
For liquid single-phase and visually homogeneous samples (with no visible particles).
When not to use it
For liquid samples where particles or emulsions can be visually identified, including sludge and slurries.
Procedure
Stir with appropriate tool or shake the closed bottle.
A.2.3.2 Mechanical homogenisation
When to use it
For liquid samples, possibly containing small particles like sludge or slurry, that don not settle or form
layers within minutes;
for liquid samples, containing more than one layer when emulsions may be formed.
When not to use it
For liquid samples containing particles that are too large to be homogenised and/or settle within minutes
after homogenisation, forming layers. In this case, homogenisation is not possible, separate and treat
each phase as a different sample (see A.3 phase/fraction separation);
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for liquid samples, containing more than one layer when phase separation occurs instantaneously.
Procedure
Different types of mechanical mixers (impeller, magnetic stirrer, propeller, ultrasonic, emulsifier etc.) can be
used, depending on the properties of the sample. The sub-sample shall be taken out as quickly as possible
just after the homogenisation, in order to avoid settling or phase separation.
A.2.4 Homogenisation in case of volatile compounds
If volatile compounds of interest are expected in the sample homogenisation has to be done very carefully and
quickly to avoid losses. If losses cannot be avoided during homogenisation process it may be a solution to
take several non-homogenised sub-samples for analyses of volatile compounds and calculate the statistical
mean as an estimate of the total content. This step should not lead to major alterations of the composition and
the representativity of the remaining sample. A possible procedure for volatile organic compounds is given in
ISO 14507:2003, 8.2.
NOTE The sampling plan should consider the presence of volatile compounds.
A.3 Phase/fraction separation
A.3.1 General information
For heterogeneous and multi-phase samples, depending on their nature and on the determinations of interest,
one or more techniques of phase separation can be applied to obtain two or more different sub-samples that
are to be analysed separately. For samples consisting of different fractions, separation of some fractions may
be necessary (e.g. nuts, bolts, stones). For this reason, the weight of each separated phase (sub-sample)
shall be directly or indirectly measured after the separation, in order to allow a final weighed combination of
different phases analysis results.
The test report shall clearly state the technique(s) used for phase separation, the weight and analytical results
related to all sub-samples obtained from phase separation, as well as the “weighted” results.
A.3.2 Solid – liquid separation
Depending on the nature of the sample and the analytical techniques to be used, one or more of the following
separation techniques can be applied.
A.3.2.1 Settling
When to use it
In every case, provided that complete separation of the two phases can be reached in appropriate time
without alterations of analytes of interest.
NOTE 1 Settling with appropriate cooling may be the method of choice, if volatile compounds are to be analysed in
the sample.
When not to use it
When the properties of the sample don’t allow a good separation of the phases in a reasonable time;
if it is necessary to recover the maximum amount possible of liquid phase, or when it’s necessary to
obtain a solid phase that is as dry as possible, because normally a certain amount of water is still present
in the settled phase;
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when biological or chemical alterations are expected during settling time.
NOTE 2 A reasonable time could be a maximum time of two hours.
Procedure
Let the bottles stand undisturbed until the phases can be separated with an appropriate technique.
A.3.2.2 Filtration
When to use it
When other solid-liquid separation techniques fail or are practically n
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