SIST EN 13656:2004
(Main)Characterization of waste - Microwave assisted digestion with hydrofluoric (HF), nitric (HNO3) and hydrochloric (HCl) acid mixture for subsequent determination of elements
Characterization of waste - Microwave assisted digestion with hydrofluoric (HF), nitric (HNO3) and hydrochloric (HCl) acid mixture for subsequent determination of elements
This European Standard specifies methods of microwave assisted digestion with hydrofluoric (HF), nitric (HNO3)and hydrochloric (HCL) acid mixture. Solutions produced by the methods are suitable for analysis e.g.by atomic absorption spectometry (FLAAS,HGAAS,CVAAS,GFAAS), inductively coupled plasma emission spectometry(ICP-OES) and inductive coupled plasma mass spectometry(ICP-MS). The method is applicable to the microwave assisted acid digestion of waste for example for the following elements:Al,Sb,As,B,Ba,Be,Cd,Cr,Cu,Fe,Pb,Mg,Mn,Hg,Mo, Ni,P,K,Se,Ag,S,Na,Sr,Te,Ti,Tl,V,Zn.
Charakterisierung von Abfällen - Aufschluss mittels Mikrowellengerät mit einem Gemisch aus Fluorwasserstoffsäure (HF), Salpetersäure (HNO3) und Salzsäure (HCI) für die anschließende Bestimmung der Elemente im Abfall
Diese Norm legt Verfahren für den Aufschluß mittels Mikrowellengerät mit einem Gemisch aus Fluorwasserstoffsäure, Salpetersäure und Salzsäure fest. Die nach den Verfahren hergestellten Lösungen sind z.B. für Analysen mittels Flammen-Atomabsorptionsspektrometrie (FAAS), Hydrid-Atomabsorptions- spektrometrie (HGAAS), Kaltdampf-Atomabsorptionsspektrometrie (CVAAS), Graphitrohrofen-Atomabsorptionsspektrometrie (GFAAS), optischer Emissions- spektrometrie mit induktiv gekoppeltem Plasma (ICP-OES) und induktiv gekoppelterPlasma-Emission-Massenspektrometrie (ICP-MS) geeignet.
Caractérisation des déchets - Digestion assistée par micro-ondes avec un mélange d'acides fluorhydrique (HF), nitrique (HNO3) et chlorhydrique (HCI) pour la détermination ultérieure d'éléments contenus dans les déchets
La présente Norme européenne décrit des méthodes de digestion assistée par micro-ondes avec un mélange d'acides fluorhydrique (HF), nitrique (HNO3) et chlorhydrique (HCl). Les solutions produites par ces méthodes conviennent a l'analyse, par exemple par spectrométrie d'absorption atomique (FLAAS, HGAAS, CVAAS, GFAAS), spectrométrie d'émission par un plasma a couplage inductif (ICP-OES) et spectrométrie de masse par un plasma a couplage inductif (ICP-MS).
La méthode est applicable pour la digestion acide assistée par micro-ondes des déchets, par exemple pour les éléments suivants : Al, Sb, As, B, Ba, Be, Ca, Cd, Cr, Co, Cu, Fe, Pb, Mg, Mn, Hg, Mo, Ni, P, K, Se, Ag, S, Na, Sr, Sn, Te, Ti, Tl, V, Zn.
Karakterizacija odpadkov - Mikrovalovni razklop z zmesjo fluorovodikove (HF), klorovodikove (HCl) in dušikove(V) kisline (HNO3) za določanje elementov
General Information
Relations
Standards Content (Sample)
SLOVENSKI STANDARD
SIST EN 13656:2004
01-januar-2004
.DUDNWHUL]DFLMDRGSDGNRY0LNURYDORYQLUD]NORS]]PHVMRIOXRURYRGLNRYH +)
NORURYRGLNRYH +&O LQGXãLNRYH 9 NLVOLQH +12 ]DGRORþDQMHHOHPHQWRY
Characterization of waste - Microwave assisted digestion with hydrofluoric (HF), nitric
(HNO3) and hydrochloric (HCl) acid mixture for subsequent determination of elements
Charakterisierung von Abfällen - Aufschluss mittels Mikrowellengerät mit einem Gemisch
aus Fluorwasserstoffsäure (HF), Salpetersäure (HNO3) und Salzsäure (HCI) für die
anschließende Bestimmung der Elemente im Abfall
Caractérisation des déchets - Digestion assistée par micro-ondes avec un mélange
d'acides fluorhydrique (HF), nitrique (HNO3) et chlorhydrique (HCI) pour la détermination
ultérieure d'éléments contenus dans les déchets
Ta slovenski standard je istoveten z: EN 13656:2002
ICS:
13.030.40 Naprave in oprema za Installations and equipment
odstranjevanje in obdelavo for waste disposal and
odpadkov treatment
SIST EN 13656:2004 en
2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.
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EUROPEAN STANDARD
EN 13656
NORME EUROPÉENNE
EUROPÄISCHE NORM
October 2002
ICS 13.030.40
English version
Characterization of waste - Microwave assisted digestion with
hydrofluoric (HF), nitric (HNO ) and hydrochloric (HCl) acid
3
mixture for subsequent determination of elements
Caractérisation des déchets - Digestion assistée par micro- Charakterisierung von Abfällen - Aufschluss mittels
ondes avec un mélange d'acides fluorhydrique (HF), Mikrowellengerät mit einem Gemisch aus
nitrique (HNO ) et chlorhydrique (HCI) pour la Fluorwasserstoffsäure (HF), Salpetersäure (HNO ) und
3 3
détermination ultérieure d'éléments contenus dans les Salzsäure (HCI) für die anschließende Bestimmung der
déchets Elemente im Abfall
This European Standard was approved by CEN on 19 August 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 13656:2002 E
worldwide for CEN national Members.
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EN 13656:2002 (E)
Contents
page
Foreword . 3
1 Scope. 5
2 Normative references . 5
3 Terms and definitions. 5
4 Safety remarks . 6
5 Sample. 6
5.1 Sample pre-treatment. 6
5.2 Mass of test portion . 7
6 Equipment. 7
6.1 Closed vessel system . 7
6.1.1 Microwave unit. 7
6.1.2 Digestion vessels . 7
6.2 Semi-open vessel system. 7
6.2.1 Microwave unit. 7
6.2.2 Digestion vessels . 8
6.3 General equipment . 8
7 Reagents . 8
8 Interferences and sources of error . 8
8.1 General informations . 8
8.2 Closed vessel system . 9
8.3 Semi-open vessel system. 9
9 Procedure. 9
9.1 Blank test . 9
9.2 Procedure for closed vessels. 9
9.2.1 Amount of samples and reagents. 10
9.2.2 Digestion. 10
9.2.3 Complexation of HF. 10
9.2.4 Preparation of the solution for analysis . 10
9.3 Procedure for semi-open vessels . 11
9.3.1 Amount of samples. 11
9.3.2 Digestion and complexation of HF . 11
9.3.3 Preparation of the solution for analysis . 11
10 Test report. 12
Annex A (normative) Calibration of the power adjustment. 13
Annex B (informative) Validation. 14
Bibliography. 25
2
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EN 13656:2002 (E)
Foreword
This document EN 13656:2002 has been prepared by Technical Committee CEN/TC 292 "Characterization 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 April 2003, and conflicting national standards shall be withdrawn at the latest
by April 2003.
In this European Standard the annex A is normative and the annexe B is 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.
3
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EN 13656:2002 (E)
Introduction
The purpose of the method is to bring the elements to be determined in many types of waste into solution to
provide a rapid digestion for analysis. Elements extractable by this procedure can in many instances be described
as „total“. On another hand they cannot be regarded as available for leaching, as the extraction procedure is too
vigorous to represent natural processes.
4
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EN 13656:2002 (E)
1 Scope
This European Standard specifies methods of microwave assisted digestion with hydrofluoric (HF), nitric (HNO )
3
and hydrochloric (HCl) acid mixture. Solutions produced by the methods are suitable for analysis e.g. by atomic
absorption spectrometry (FLAAS, HGAAS, CVAAS, GFAAS), inductively coupled plasma emission spectrometry
(ICP-OES) and inductive coupled plasma mass spectrometry (ICP-MS).
The method is applicable to the microwave assisted acid digestion of waste for example for the following
elements: Al, Sb, As, B, Ba, Be, Ca, Cd, Cr, Co, Cu, Fe, Pb, Mg, Mn, Hg, Mo, Ni, P, K, Se, Ag, S, Na, Sr, Sn, Te,
Ti, Tl, V, Zn.
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 ISO 3696:1995, 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
digestion
mineralization of the organic matter of a sample and dissolution of its mineral part, more or less completely, when
reacted with a reagent mixture
3.2
sample
portion of material selected from a larger quantity of material
[ENV 12506:2001]
3.3
laboratory sample
sample or sub-sample(s) sent to or received by the laboratory
[ENV 12506:2001]
3.4
test sample; analytical sample
sample, prepared from the laboratory sample, from which test portions are removed for testing or analysis
[ENV 12506:2001]
3.5
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
[ENV 12506:2001]
NOTE 1 The test portion may be taken from the laboratory sample directly if no preparation of sample is required (e.g. with
liquids), but usually it is taken from the prepared test sample.
5
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EN 13656:2002 (E)
NOTE 2 A unit or increment of proper homogeneity, size and fineness, needing no further preparation, may be a test portion.
3.6
dry residue
dry matter expressed as a percentage by mass after drying at 105 °C ± 5 °C to the constancy of weight
3.7
digestion vessel
special flask where the test portion and the acid mixture are filled in and the digestion is performed
3.8
microwave unit
whole microwave digestion system (oven and associated equipment)
3.9
microwave unit cavity
inner part of the microwave unit in which the digestion vessel is located and the microwave digestion is performed
3.10
focused microwave unit
microwave unit in which a precise control of the electric field is made by using a wave guide
NOTE Microwaves are focused at the bottom part of the digestion vessel.
4 Safety remarks
All this work has to be performed by skilled persons.
The reagents used within this European Standard are strongly corrosive and partly very toxic. Safety precautions
are absolutely necessary due to strong corrosive reagents, high temperature and high pressure.
All procedures have to be performed in a hood or in closed force-ventilated equipment. By the use of strong
oxidising reagents the formation of explosive organic intermediates is possible especially when dealing with
samples with a high organic content. Do not open pressurised vessels before they have cooled down. Avoid
contact with the chemicals and the gaseous reaction products. Samples and solutions have to be disposed of
according to regulations.
People performing the test shall be informed on the specific risk of HF.
5 Sample
5.1 Sample pre-treatment
The test portion should be transferred into the vessel as it is without any pre-treatment if possible.This is
applicable only if the test portion is representative for the laboratory sample and the effectiveness of the digestion
is proven.
If these conditions are not met a pre-treatment of the laboratory sample is necessary. This procedure shall not
change the concentration of the elements of interest.
NOTE Pre-treatment may include drying or grain size reduction below a particle size of 250 μm for solid waste or
homogenizing by use of a high speed mixer or sonification for liquid samples.
The mass of laboratory samples shall be sufficient for the multiple digestion procedures and determination of the
dry residue.
6
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EN 13656:2002 (E)
5.2 Mass of test portion
The mass of test portion for a single digestion has to be selected in a way, that:
— it is representative for the laboratory sample;
— it complies with the specifications of manufacturer of the digestion unit.
NOTE If the representative test portion exceeds the manufacturers specifications the test portion should be devided into
smaller quantities and digested seperately. The individual digests should be combined prior to analysis.
For representativity reason mass above 200 mg is to be preferred. Unless recommended by the manufacturer the
amount of organic carbon shall not exceed 100 mg because of safety reasons in the case of closed digestion
vessel.
6 Equipment
6.1 Closed vessel system
6.1.1 Microwave unit
The microwave unit shall provide programmable power which can be programmed to within ± 10 W of the
required power. Typical units provide a nominal 600 W to 1 200 W of power. If necessary (referring to
manufactures specifications) calibration of the microwave unit has to be performed (see annex A).
The microwave unit has to comply to European and national regulations relevant to microwave radiation.
The microwave unit cavity has to be well ventilated. It has to have an exhaust air tube which is connected to a
corrosion resistant laboratory air outlet system or the instrument is provided for use in a laboratory hood.
All electronics are sufficiently protected against corrosion for safe operation. All parts which can have contact with
acids or their vapours have to be corrosion resistant.
The microwave unit shall be designed in a way that guarantees homogeneous heating of the samples.
The microwave unit cavity has to be built in a way that even in case of leakage or explosion of the vessels the
safety of the operators can be guaranteed. Household instruments are not suitable for laboratory use.
NOTE The microwave unit should include a temperature and/or pressure control system.
6.1.2 Digestion vessels
The vessels used in the microwave unit shall be equiped with a pressure relieve valve or another technical
equipment which avoids the bursting of the vessels at suddenly occuring excess pressure. The material of the
vessels has to be inert to the acids used for digestion. The digestion vessel shall withstand the pressure of at
least 8 bar. If the amount of organic carbon exceeds 100 mg it has to be ensured that the digestion vessel is
capable of withstanding higher pressures.
6.2 Semi-open vessel system
6.2.1 Microwave unit
The microwave unit shall be equiped with power control. Typical unit provides a nominal 200 W or 300 W of
released power. If necessary, calibration of the microwave unit has to be performed by the manufacturer.
The microwave unit shall comply with European and national regulations relevant to microwave radiation.
7
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EN 13656:2002 (E)
The microwave unit shall be designed for use in a laboratory hood.
Fume extraction equipment, used to extract acid vapours from the reaction vessels during the digestion
programme, shall have sufficient flow rate to prevent the release of dangerous vapours into the laboratory.
All electronics shall be sufficiently protected against corrosion for safe operation. All parts which can be in contact
with acids or their vapours shall be corrosion resistant.
6.2.2 Digestion vessels
The vessel is working at atmospheric pressure and has to be connected with a reflux system to avoid losses of
analytes. The vessel shall comply with the manufactures specifications and should have a minimum volume of
50 ml.
The material of the vessels has to be inert to the reagents used for digestion.
NOTE Quartz or borosilicated glass digestion vessels are not useable when hydrofluoric acid is used. For example
polytetrafluorethylen (PTFE) digestion vessels can be used.
6.3 General equipment
The following equipment is used by both systems described in 6.1 and 6.2:
— volumetric graduated flasks and pipettes of adequate size;
— filter equipment of adequate chemical resistance and purity or centrifuge;
— analytical balance, with an error limit of – 0,1 mg.
For the preparation of standards and the treatment and storage of samples for determination of boron, the use of
borosilicate glass shall be avoided.
The use of glass ware shall be excluded when free hydrofluoric acid is present.
7 Reagents
Use reagents of analytical grade quality or better and water of grade 1 according to EN ISO 3696:1995.
— Hydrochloric acid (HCl): a mass fraction of 35 % to 37 %;
— Nitric acid (HNO ): a mass fraction of 65 % to 70 %;
3
— Hydrofluoric acid (HF): a mass fraction of 40 % to 45 %;
— Boric acid (B(OH) ): solid.
3
8 Interferences and sources of error
8.1 General informations
Due to the volatility of some compounds it is of great importance to take care, that the sample is not heated
before the digestion and that the volatile reaction products which might be formed during the digestion are not
allowed to escape.
8
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EN 13656:2002 (E)
The container in which the sample is delivered and stored can be a source of errors. Its material shall be chosen
according to the elements to be determined (e.g. elemental Hg can penetrate polyethylene walls very fast in both
directions. Glass can contaminate samples with elements contained: e.g. B, Na, K, Al)
Grinding or milling samples includes a risk of contamination of the sample by the environment (air, dust, wear of
milling equipment). Due to elevate temperature losses of volatile compounds are possible.
For the determination of elements forming volatile compounds (e.g. Hg, As, Pb) special care has to be taken at
sample pre-treatment.
The use of the described digestion procedure may leave parts of the sample undissolved. This includes the risk of
low recoveries and of bad repeatability. If required the residue can be analysed separately e.g. by alkaline fusion.
High acid and solute concentration in the digest solution can cause interferences at determination. Depending on
the content of the digest solution some equipment for determination is not applicable.
Depending on the concentration of the element of interest and the wanted precision, a particular caution to the
cleaning of the vessels shall be taken. It is recommended to clean the vessels with 10 % nitric acid.
Care shall be taken to ensure that all of the test portion is brought into contact with the acid mixture in the reaction
vessel.
Some elements of interest can be lost because of precipitation with some ions of the solution. It is the case for
insoluble chlorides, fluorides and sulphates for example. In this case the precipitate can be analysed separately.
In the case of filtration of the digested solution it is necessary to take care that the filtration procedure does not
introduce contaminants.
8.2 Closed vessel system
The upper limits of mass of the test portion referring to the manufacturers specifications have to be taken into
account.
Very reactive or volatile materials that may create high pressures when heated may cause a venting of the
vessels with potential loss of sample and analytes. The complete decomposition of either carbonates, or carbon
based samples, may cause enough pressure to vent the vessel.
After digestion, the vessel shall be cooled to room temperature before opening. If not, losses of certain elements,
particulary volatile elements as mercury or arsenic can occur.
8.3 Semi-open vessel system
Depending on the volatility of some elements of interest, the reflux system can be inefficient to condense the
vapours and losses of some elements of interest can happen.
9 Procedure
9.1 Blank test
To detect possible contaminations from vessels and/or reagents, blank tests shall be carried out in parallel by the
same digestion procedure and filtration if appropriate, using the same quantities of all reagents but omitting the
test portion.
9.2 Procedure for closed vessels
The following description have to be done step by step:
9
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EN 13656:2002 (E)
9.2.1 Amount of samples and reagents
Weigh between 0,2 g to 0,5 g of the sample, to the nearest 0,1 mg, prepared according to clause 5 and transfer it
into the vessel. If necessary the sample may be moistened with a minimum amount of water. Then add seperately
6 ml HCl, 2 ml HNO and 2 ml HF.
3
It is necessary to use only one specific reaction mixture as well as the same kind of matrix in the same quantity of
test portion in a single batch in the microwave unit cavity to ensure consistent reaction conditions.
If a vigorous reaction occurs, allow the reaction to lie down before capping the vessel.
9.2.2 Digestion
Transfer the digestion vessels into the microwave unit cavity according to the manufactures instructions and start
the following digestion procedure.
Table 1 — Power programme
Time Power
min W
2 250
20
5 250
5 400
5 500
The power programme (see Table 1) is intended to be used for batches of 6 samples. Commercial available
microwave units may contain more or less sample positions. In order to ensure consistant reaction conditions in
these cases the power programme has to be adjusted according to the manufactures instructions. For batches
where all positions are not occupied either the empty positions shall be filled up with e.g. blanks or duplicates or
the power programme shall be adjusted in accordance with the number of samples.
At the end of the programme let the vessels cool down to room temperature. Confirm that no losses of digestion
solution occured during the procedure (e.g. by control of burstmembran referring to the manufactures
specifications or controll of mass). Otherwise the samples have to be discarded.
9.2.3 Complexation of HF
Carefully uncap and vent each vessel in a fume hood, then add a solution containing 650 mg of boric acid (e.g.
22 ml of 4 % m/m). Cap the vessels and put them into the microwave unit cavity and start the following
programme:
— time 3 min ;
— power 300 W.
At the end of the programme let the vessels cool down to room temperature.
In this step the boron determination shall not be performed. In this case ensure that HF concentration in solution
is low enough to avoid damage to measurement systems.
9.2.4 Preparation of the solution for analysis
Carefully uncap and vent each vessel in a fume hood, then transfer quantitatively the content of the vessels into a
suitable sized volumetric flask and fill up to the mark.
10
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EN 13656:2002 (E)
If the digested sample contains particles which might clog the nebulizers of the measurement apparatus or which
might interfere with the injection of the sample into the instrument, the sample solution may be centrifuged,
allowed to settle or be filtered. In the case of filtration, dilute the content of the vessel before filtering, rinse and
then fill to the mark of the volumetric flask. The method used has to be reported in the test report.
9.3 Procedure for semi-open vessels
9.3.1 Amount of samples
Weigh between 0,2 g to 1,0 g of the sample, to the nearest 0,1 mg, prepared according to clause 5 and transfer it
into the vessel. If necessary the sample may be moistened with a minimum amount of water.
9.3.2 Digestion and complexation of HF
Transfer the digestion vessels into the microwave unit cavity according to the manufactures instructions and start
the following digestion procedure (see Table 2).
Table 2 — Microwave programme
Step Acid Volume Power Time
ml W min
1 HCl 3 0 0
2 HNO 10 0
3
3 HF 5 70 10
4 HNO 570 5
3
5 HNO 570 5
3
6 HCl 5 70 5
7H BO (4 % m/m) 40 70 5
3 3
It is necessary not to let the digested solution cool down between the step 6 and the step 7. If the solution is
cooled down between these two steps, the heating step 7 shall last 10 min.
For boron determination step 7 shall not be executed. In this case ensure that HF concentration in solution is low
enough to avoid damage to measurement systems.
NOTE Introduction of the digestion vessel into the microwave cavity, reagent injection into the digestion vessel, temperature
and/or power control can be done automatically or manually depending on the apparatus used.
At the end of the programme, let the vessels cool down to room temperature.
9.3.3 Preparation of the solution for analysis
Transfer quantitatively the solution content of each vessel into a suitable sized volumetric flask and dilute to the
mark.
If the digested mixture contains particles which might clog the nebulizers of the measurement apparatus or which
might interfere with the injection of the sample into the instrument, the sample may be centrifuged, allowed to
settle or be filtered. In the case of filtration, dilute the content of the vessel before filtering, rinse and then dilute to
the mark of the volumetric flask. The method used has to be reported in the test report.
11
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EN 13656:2002 (E)
10 Test report
The work carried out by the testing laboratory shall be covered by a report which accurately, clearly and
unambiguously presents the test results and all other relevant informations.
The test report shall include at least the following information:
a) a reference to this European Standard;
b) name and address of the testing laboratory and location where the test was carried out when different from the
address of the testing laboratory;
c) unique identification of report (such as serial number) and of each page, and total number of pages of the
report;
d) identification and description of the laboratory sample(s);
e) quantity and date of receipt of the laboratory sample(s) and date(s) of performance of the test;
f) relevant information about the digestion procedure and the sample(s):
— quantity of each test portion;
— sample(s) pre-treatment (e.g. drying, milling);
— reference to the actual digestion method (e.g. digestion system, reagents, microwave programme);
— technique used for the separation of the solid residue, if any (e.g. centrifugation, filtering);
— description and reasons for any deviation from the standard procedures;
— method and result of dry matter determination;
g) a signature and title or an equivalent marking of person(s) accepting technical responsibility for the test report
and date of issue;
h) a statement, that the information contained in the report relate exclusively to the laboratory
sample(s) tested;
i) a statement that the report shall not be reproduced except in full without the written approval of the testing
laboratory;
The
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