SIST EN ISO 14855-1:2013

Determination of the ultimate aerobic biodegradability of plastic materials under controlled composting conditions - Method by analysis of evolved carbon dioxide - Part 1: General method (ISO 14855-1:2012)

This part of ISO 14855 specifies a method for the determination of the ultimate aerobic biodegradability of plastics, based on organic compounds, under controlled composting conditions by measurement of the amount of carbon dioxide evolved and the degree of disintegration of the plastic at the end of the test. This method is designed to simulate typical aerobic composting conditions for the organic fraction of solid mixed municipal waste. The test material is exposed to an inoculum which is derived from compost. The composting takes place in an environment wherein temperature, aeration and humidity are closely monitored and controlled. The test method is designed to yield the percentage conversion of the carbon in the test material to evolved carbon dioxide as well as the rate of conversion. Subclauses 8.6 and 8.7 specify a variant of the method, using a mineral bed (vermiculite) inoculated with thermophilic microorganisms obtained from compost with a specific activation phase, instead of mature compost. This variant is designed to yield the percentage of carbon in the test substance converted to carbon dioxide and the rate of conversion. The conditions described in this part of ISO 14855 may not always correspond to the optimum conditions for the maximum degree of biodegradation to occur.

Bestimmung der vollständigen aeroben Bioabbaubarkeit von Kunststoff-Materialien unter den Bedingungen kontrollierter Kompostierung - Verfahren mittels Analyse des freigesetzten Kohlenstoffdioxides - Teil 1: Allgemeines Verfahren (ISO 14855-1:2012)

Dieser Teil der ISO 14855 legt ein Verfahren fest, mit dem unter geregelten Kompostierbedingungen durch Messung der Menge des gebildeten Kohlendioxids und des Grades des Zerfalls des Kunststoffs am Ende der Prüfung die vollständige aerobe Bioabbaubarkeit von Kunststoffen, die auf organischen Verbindungen beruhen, bestimmt wird. Dieses Verfahren ist dafür ausgelegt, typische aerobe Kompostierbedingungen für den organischen Anteil in festem gemischtem städtischem Abfall zu simulieren. Die Prüfsubstanz wird einem Inokulum ausgesetzt, das aus Kompost gewonnen wird. Die Kompostierung erfolgt in einer Umgebung, in der Temperatur, Begasung und Feuchte genau überwacht und geregelt werden. Das Prüfverfahren dient der Feststellung der prozentualen Umwandlung des Kohlenstoffs in der Prüfsubstanz in freigesetztes Kohlendioxid sowie der Geschwindigkeit dieser Umwandlung.
Die Unterabschnitte 8.6 und 8.7 legen eine Variante des Verfahrens fest, bei der anstelle des ausgereiften Kompostes ein mineralisches Festbett (Vermiculit) mit thermophilen Mikroorganismen, die aus dem Kompost innerhalb einer spezifischen Aktivierungsphase gewonnen werden, beimpft wird. Diese Variante wurde entwickelt, um den prozentualen Anteil des in Kohlendioxid umgewandelten Kohlenstoffs in der Prüfsubstanz und die Geschwindigkeit dieser Umwandlung festzustellen.
Die in diesem Teil der ISO 14855 beschriebenen Bedingungen entsprechen möglicherweise nicht immer den optimalen Bedingungen, unter denen der maximale Grad an Bioabbau erreicht wird.

Évaluation de la biodégradabilité aérobie ultime des matériaux plastiques dans des conditions contrôlées de compostage - Méthode par analyse du dioxyde de carbone libéré - Partie 1: Méthode générale (ISO 14855-1:2012)

Določanje končne aerobne biorazgradljivosti in razkroja polimernih materialov pod nadzorovanimi pogoji kompostiranja - Metoda z analizo sproščenega ogljikovega dioksida - 1. del: Splošna metoda (ISO 14855-1:2012)

Ta del standarda ISO 14855 določa metodo za določanje končne aerobne biorazgradljivosti in razkroja polimernih materialov, ki temeljijo na organskih sestavinah, pod nadzorovanimi pogoji kompostiranja z merjenjem količine sproščenega ogljikovega dioksida in stopnje razkroja polimernih materialov na koncu preskusa. Ta metoda je izdelana za simulacijo značilnih aerobnih pogojev kompostiranja organskega deleža trdnih mešanih komunalnih odpadkov. Preskusni material je izpostavljen inokulumu, ki izhaja iz komposta. Kompostiranje poteka v okolju, kjer so temperatura, zračnost in vlaga natančno spremljane in nadzorovane. Preskusna metoda je izdelana tako, da proizvede odstotek pretvorbe ogljika iz preskusnega materiala v sproščeni ogljikov dioksid ter tudi stopnjo pretvorbe. V točkah 8.6 in 8.7 je navedena različica metode, ki uporablja vermikulit z vcepljenimi termofilnimi mikroorganizmi, ki se namesto iz zrelega komposta pridobijo iz komposta z določeno fazo aktiviranja. Ta metoda je izdelana tako, da proizvede odstotek ogljika v preskusni snovi, ki se pretvori v ogljikov dioksid, in stopnjo pretvorbe. Pogoji, ki so opisani v tem delu standarda ISO 14855 niso vedno enaki idealnim pogojem, kjer pride do največje stopnje biorazgradljivosti.

General Information

• Status: Published
• Publication Date: 03-Jun-2013
• ICS: 13.030.99 - Other standards related to wastes
• ICS: 83.080.01 - Plastics in general
• Technical Committee: IPMA - Polimer materials and products
• Current Stage: 6060 - National Implementation/Publication (Adopted Project)
• Start Date: 03-Jun-2013
• Due Date: 08-Aug-2013
• Completion Date: 04-Jun-2013
• Ref Project: EN ISO 14855-1:2012 - Determination of the ultimate aerobic biodegradability of plastic materials under controlled composting conditions - Method by analysis of evolved carbon dioxide - Part 1: General method (ISO 14855-1:2012)

RELATIONS

• Revised: SIST EN ISO 14855-1:2007 - Determination of the ultimate aerobic biodegradability of plastic materials under controlled composting conditions - Method by analysis of evolved carbon dioxide - Part 1: General method (ISO 14855-1:2005)
• Effective Date: 11-Dec-2010
• Replaces: SIST EN ISO 14855-1:2007/AC:2010 - Determination of the ultimate aerobic biodegradability of plastic materials under controlled composting conditions - Method by analysis of evolved carbon dioxide - Part 1: General method (ISO 14855-1:2005/Cor 1:2009)
• Effective Date: 01-Jul-2013
• Replaces: SIST EN ISO 14855-1:2007 - Determination of the ultimate aerobic biodegradability of plastic materials under controlled composting conditions - Method by analysis of evolved carbon dioxide - Part 1: General method (ISO 14855-1:2005)
• Effective Date: 01-Jul-2013

Standards Content (sample)

SLOVENSKI STANDARD
SIST EN ISO 14855-1:2013
01-julij-2013
1DGRPHãþD
SIST EN ISO 14855-1:2007
SIST EN ISO 14855-1:2007/AC:2010

'RORþDQMHNRQþQHDHUREQHELRUD]JUDGOMLYRVWLLQUD]NURMDSROLPHUQLKPDWHULDORYSRG

QDG]RURYDQLPLSRJRMLNRPSRVWLUDQMD0HWRGD]DQDOL]RVSURãþHQHJDRJOMLNRYHJD
GLRNVLGDGHO6SORãQDPHWRGD,62

Determination of the ultimate aerobic biodegradability of plastic materials under

controlled composting conditions - Method by analysis of evolved carbon dioxide - Part 1:

General method (ISO 14855-1:2012)
Bestimmung der vollständigen aeroben Bioabbaubarkeit von Kunststoff-Materialien

unter den Bedingungen kontrollierter Kompostierung - Verfahren mittels Analyse des

freigesetzten Kohlenstoffdioxides - Teil 1: Allgemeines Verfahren (ISO 14855-1:2012)

Évaluation de la biodégradabilité aérobie ultime des matériaux plastiques dans des

conditions contrôlées de compostage - Méthode par analyse du dioxyde de carbone
libéré - Partie 1: Méthode générale (ISO 14855-1:2012)
Ta slovenski standard je istoveten z: EN ISO 14855-1:2012
ICS:
13.030.99 Drugi standardi v zvezi z Other standards related to
odpadki wastes
83.080.01 Polimerni materiali na Plastics in general
splošno
SIST EN ISO 14855-1:2013 en,fr,de

2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.

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SIST EN ISO 14855-1:2013
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SIST EN ISO 14855-1:2013
EUROPEAN STANDARD
EN ISO 14855-1
NORME EUROPÉENNE
EUROPÄISCHE NORM
December 2012
ICS 83.080.01 Supersedes EN ISO 14855-1:2007
English Version
Determination of the ultimate aerobic biodegradability of plastic
materials under controlled composting conditions - Method by
analysis of evolved carbon dioxide - Part 1: General method
(ISO 14855-1:2012)

Évaluation de la biodégradabilité aérobie ultime des Bestimmung der vollständigen aeroben Bioabbaubarkeit

matériaux plastiques dans des conditions contrôlées de von Kunststoff-Materialien unter den Bedingungen

compostage - Méthode par analyse du dioxyde de carbone kontrollierter Kompostierung - Verfahren mittels Analyse

libéré - Partie 1: Méthode générale (ISO 14855-1:2012) des freigesetzten Kohlenstoffdioxides - Teil 1: Allgemeines

Verfahren (ISO 14855-1:2012)
This European Standard was approved by CEN on 13 November 2012.

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 CEN-CENELEC 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 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, Former Yugoslav Republic of Macedonia, France, Germany, Greece, Hungary, Iceland, Ireland, Italy, Latvia, Lithuania,

Luxembourg, Malta, Netherlands, Norway, Poland, Portugal, Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland, Turkey and United

Kingdom.
EUROPEAN COMMITTEE FOR STANDARDIZATION
COMITÉ EUROPÉEN DE NORMALISATION
EUROPÄISCHES KOMITEE FÜR NORMUNG
Management Centre: Avenue Marnix 17, B-1000 Brussels

© 2012 CEN All rights of exploitation in any form and by any means reserved Ref. No. EN ISO 14855-1:2012: E

worldwide for CEN national Members.
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SIST EN ISO 14855-1:2013
EN ISO 14855-1:2012 (E)
Contents Page

Foreword ..............................................................................................................................................................3

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SIST EN ISO 14855-1:2013
EN ISO 14855-1:2012 (E)
Foreword

This document (EN ISO 14855-1:2012) has been prepared by Technical Committee ISO/TC 61 "Plastics" in

collaboration with Technical Committee CEN/TC 249 “Plastics” the secretariat of which is held by NBN.

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 June 2013, and conflicting national standards shall be withdrawn at

the latest by June 2013.

Attention is drawn to the possibility that some of the elements of this document may be the subject of patent

rights. CEN [and/or CENELEC] shall not be held responsible for identifying any or all such patent rights.

This document supersedes EN ISO 14855-1:2007.

According to the CEN/CENELEC Internal Regulations, the national standards organisations of the following

countries are bound to implement this European Standard: Austria, Belgium, Bulgaria, Croatia, Cyprus, Czech

Republic, Denmark, Estonia, Finland, Former Yugoslav Republic of Macedonia, France, Germany, Greece,

Hungary, Iceland, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta, Netherlands, Norway, Poland, Portugal,

Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland, Turkey and the United Kingdom.

Endorsement notice

The text of ISO 14855-1:2012 has been approved by CEN as a EN ISO 14855-1:2012 without any

modification.
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SIST EN ISO 14855-1:2013
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SIST EN ISO 14855-1:2013
INTERNATIONAL ISO
STANDARD 14855-1
Second edition
2012-12-01
Determination of the ultimate aerobic
biodegradability of plastic materials
under controlled composting
conditions — Method by analysis of
evolved carbon dioxide —
Part 1:
General method
Évaluation de la biodégradabilité aérobie ultime des matériaux
plastiques dans des conditions contrôlées de compostage — Méthode
par analyse du dioxyde de carbone libéré —
Partie 1: Méthode générale
Reference number
ISO 14855-1:2012(E)
ISO 2012
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SIST EN ISO 14855-1:2013
ISO 14855-1:2012(E)
COPYRIGHT PROTECTED DOCUMENT
© ISO 2012

All rights reserved. Unless otherwise specified, no part of this publication may be reproduced or utilized in any form or by any means,

electronic or mechanical, including photocopying and microfilm, without permission in writing from either ISO at the address below or ISO’s

member body in the country of the requester.
ISO copyright office
Case postale 56 • CH-1211 Geneva 20
Tel. + 41 22 749 01 11
Fax + 41 22 749 09 47
E-mail [e-mail]
Web www.iso.org
Published in Switzerland
ii © ISO 2012 – All rights reserved
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SIST EN ISO 14855-1:2013
ISO 14855-1:2012(E)
Contents Page

Foreword ............................................................................................................................................................................iv

Introduction ........................................................................................................................................................................ v

1 Scope ...................................................................................................................................................................... 1

2 Normative references ......................................................................................................................................... 1

3 Terms and definitions ......................................................................................................................................... 1

4 Principle ................................................................................................................................................................. 2

5 Test environment ................................................................................................................................................. 3

6 Reagents ................................................................................................................................................................ 3

6.1 TLC (thin-layer chromatography) grade cellulose ..................................................................................... 3

6.2 Vermiculite ............................................................................................................................................................. 3

7 Apparatus .............................................................................................................................................................. 4

8 Procedure .............................................................................................................................................................. 5

8.1 Preparation of the inoculum ............................................................................................................................. 5

8.2 Preparation of test material and reference material .................................................................................. 5

8.3 Start-up of the test .............................................................................................................................................. 6

8.4 Incubation period ................................................................................................................................................ 6

8.5 Termination of the test ....................................................................................................................................... 7

8.6 Use of vermiculite ............................................................................................................................................... 7

8.7 Recovery procedure and carbon balance when using vermiculite ....................................................... 8

9 Calculation and expression of results ........................................................................................................... 9

9.1 Calculation of the theoretical amount of carbon dioxide ......................................................................... 9

9.2 Calculation of the percentage biodegradation ............................................................................................ 9

9.3 Calculation of loss in mass .............................................................................................................................. 9

9.4 Expression of results ......................................................................................................................................... 9

10 Validity of results ...............................................................................................................................................10

11 Test report ...........................................................................................................................................................10

Annex A (informative) Principle of test system ........................................................................................................ 11

Annex B (informative) Examples of graphical representation of carbon dioxide evolution and

biodegradation curves .....................................................................................................................................12

Annex C (informative) Example of mass loss determination................................................................................14

Annex D (informative) Round-robin testing ...............................................................................................................16

Annex E (informative) Examples of forms .................................................................................................................17

Bibliography .....................................................................................................................................................................20

© ISO 2012 – All rights reserved iii
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SIST EN ISO 14855-1:2013
ISO 14855-1:2012(E)
Foreword

ISO (the International Organization for Standardization) is a worldwide federation of national standards bodies

(ISO member bodies). The work of preparing International Standards is normally carried out through ISO

technical committees. Each member body interested in a subject for which a technical committee has been

established has the right to be represented on that committee. International organizations, governmental and

non-governmental, in liaison with ISO, also take part in the work. ISO collaborates closely with the International

Electrotechnical Commission (IEC) on all matters of electrotechnical standardization.

International Standards are drafted in accordance with the rules given in the ISO/IEC Directives, Part 2.

The main task of technical committees is to prepare International Standards. Draft International Standards

adopted by the technical committees are circulated to the member bodies for voting. Publication as an

International Standard requires approval by at least 75 % of the member bodies casting a vote.

Attention is drawn to the possibility that some of the elements of this document may be the subject of patent

rights. ISO shall not be held responsible for identifying any or all such patent rights.

ISO 14855-1 was prepared by Technical Committee ISO/TC 61, Plastics, Subcommittee SC 5, Physical-

chemical properties.

This second edition of ISO 14855-1 cancels and replaces the first edition (ISO 14855-1:2005), of which it

constitutes a minor revision intended principally to clarify the wording of the fourth paragraph in Subclause 8.1.

In addition, the footnote to 6.2 concerning a possible supplier of “concrete” type vermiculite has been deleted

as it appeared to be no longer valid.

This second edition also cancels and replaces the Technical Corrigendum ISO 14855-1:2005/Cor.1:2009.

ISO 14855 consists of the following parts, under the general title Determination of the ultimate aerobic

biodegradability of plastic materials under controlled composting conditions — Method by analysis of evolved

carbon dioxide:
— Part 1: General method

— Part 2: Gravimetric measurement of carbon dioxide evolved in a laboratory-scale test

iv © ISO 2012 – All rights reserved
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SIST EN ISO 14855-1:2013
ISO 14855-1:2012(E)
Introduction

The main method specified in this part of ISO 14855 uses a solid-phase respirometric test system based on

mature compost used as a solid bed, a source of nutrients, and an inoculum rich in thermophilic microorganisms.

Mature compost is a very heterogeneous and complex material. Therefore, it can be difficult to quantify

the residual polymeric material left in the bed at the end of the test, to detect possible low-molecular-mass

molecules released into the solid bed by the polymeric material during degradation, and to assess the biomass.

As a result, it can be difficult to perform a complete carbon balance. Another difficulty which is sometimes

encountered with mature compost is a “priming effect”: the organic matter present in large amounts in the

mature compost can undergo polymer-induced degradation, known as the “priming effect”, which affects the

measurement of the biodegradability.

To overcome these difficulties and to improve the reliability of the method, the mature compost can be replaced

by a solid mineral medium which is used as the composting bed, thus facilitating analyses. This variant can

be used to measure the biodegradation in terms of CO evolution, to quantify and analyse the biomass and

the residues of polymeric material left in the solid bed at the end of the test, and to perform a complete carbon

balance. Furthermore, the method is not significantly affected by the priming effect and can, therefore, be used

to assess materials known to cause this problem with mature compost. The mineral bed can also be subjected

to an ecotoxicological analysis to verify the absence of any ecotoxic activity in the bed after biodegradation.

© ISO 2012 – All rights reserved v
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SIST EN ISO 14855-1:2013
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SIST EN ISO 14855-1:2013
INTERNATIONAL STANDARD ISO 14855-1:2012(E)
Determination of the ultimate aerobic biodegradability of plastic
materials under controlled composting conditions — Method by
analysis of evolved carbon dioxide —
Part 1:
General method

WARNING — Sewage, activated sludge, soil and compost may contain potentially pathogenic

organisms. Therefore appropriate precautions should be taken when handling them. Toxic test

compounds and those whose properties are unknown should be handled with care.
1 Scope

This part of ISO 14855 specifies a method for the determination of the ultimate aerobic biodegradability of

plastics, based on organic compounds, under controlled composting conditions by measurement of the amount

of carbon dioxide evolved and the degree of disintegration of the plastic at the end of the test. This method is

designed to simulate typical aerobic composting conditions for the organic fraction of solid mixed municipal

waste. The test material is exposed to an inoculum which is derived from compost. The composting takes place

in an environment wherein temperature, aeration and humidity are closely monitored and controlled. The test

method is designed to yield the percentage conversion of the carbon in the test material to evolved carbon

dioxide as well as the rate of conversion.

Subclauses 8.6 and 8.7 specify a variant of the method, using a mineral bed (vermiculite) inoculated with

thermophilic microorganisms obtained from compost with a specific activation phase, instead of mature

compost. This variant is designed to yield the percentage of carbon in the test substance converted to carbon

dioxide and the rate of conversion.

The conditions described in this part of ISO 14855 may not always correspond to the optimum conditions for

the maximum degree of biodegradation to occur.
2 Normative references

The following referenced documents are indispensable for the application of this document. For dated

references, only the edition cited applies. For undated references, the latest edition of the referenced document

(including any amendments) applies.

ISO 5663, Water quality — Determination of Kjeldahl nitrogen — Method after mineralization with selenium

ISO 8245, Water quality — Guidelines for the determination of total organic carbon (TOC) and dissolved

organic carbon (DOC)
3 Terms and definitions
For the purposes of this document, the following terms and definitions apply.
3.1
ultimate aerobic biodegradation

breakdown of an organic compound by microorganisms in the presence of oxygen into carbon dioxide, water

and mineral salts of any other elements present (mineralization) plus new biomass

© ISO 2012 – All rights reserved 1
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SIST EN ISO 14855-1:2013
ISO 14855-1:2012(E)
3.2
composting
aerobic process designed to produce compost

NOTE Compost is an organic soil conditioner obtained by biodegradation of a mixture consisting principally of

vegetable residues, occasionally with other organic material, and having a limited mineral content.

3.3
disintegration
physical breakdown of a material into very small fragments
3.4
total dry solids

amount of solids obtained by taking a known volume of test material or compost and drying at about 105 °C to

constant mass
3.5
volatile solids

amount of solids obtained by subtracting the residue of a known volume of test material or compost after

incineration at about 550 °C from the total dry solids of the same sample

NOTE The volatile-solids content is an indication of the amount of organic matter present.

3.6
theoretical amount of evolved carbon dioxide
ThCO

maximum theoretical amount of carbon dioxide evolved after completely oxidizing a chemical compound,

calculated from the molecular formula and expressed as milligrams of carbon dioxide evolved per milligram or

gram of test compound
3.7
lag phase

time, measured in days, from the start of a test until adaptation and/or selection of the degrading microorganisms

is achieved and the degree of biodegradation of a chemical compound or organic matter has increased to

about 10 % of the maximum level of biodegradation
3.8
maximum level of biodegradation

degree of biodegradation, measured in per cent, of a chemical compound or organic matter in a test, above

which no further biodegradation takes place during the test
3.9
biodegradation phase

time, measured in days, from the end of the lag phase of a test until about 90 % of the maximum level of

biodegradation has been reached
3.10
plateau phase

time, measured in days, from the end of the biodegradation phase until the end of a test

3.11
activated vermiculite

vermiculite colonized by an active microbial population during a preliminary growth phase

4 Principle

The test method determines the ultimate biodegradability and degree of disintegration of test material under

conditions simulating an intensive aerobic composting process. The inoculum used consists of stabilized,

mature compost derived, if possible, from composting the organic fraction of solid municipal waste.

2 © ISO 2012 – All rights reserved
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SIST EN ISO 14855-1:2013
ISO 14855-1:2012(E)

The test material is mixed with the inoculum and introduced into a static composting vessel where it is intensively

composted under optimum oxygen, temperature and moisture conditions for a test period not exceeding 6 months.

During the aerobic biodegradation of the test material, carbon dioxide, water, mineral salts and new microbial

cellular constituents (biomass) are the ultimate biodegradation products. The carbon dioxide produced is

continuously monitored, or measured at regular intervals, in test and blank vessels to determine the cumulative

carbon dioxide production. The percentage biodegradation is given by the ratio of the carbon dioxide produced

from the test material to the maximum theoretical amount of carbon dioxide that can be produced from the

test material. The maximum theoretical amount of carbon dioxide produced is calculated from the measured

total organic carbon (TOC) content. The percentage biodegradation does not include that amount of carbon

converted to new cell biomass which is not metabolized in turn to carbon dioxide during the course of the test.

Additionally, the degree of disintegration of the test material is determined at the end of the test, and the loss

in mass of the test material may also be determined.
Vermiculite should be used instead of mature compost

a) whenever the determination of the degree of biodegradation is affected by a priming effect induced by the

test material
and/or

b) when performing a final carbon balance with biomass determination and retrieval of the residual test material.

The vermiculite bed, being inorganic, substantially reduces the priming effect, thus improving the reliability of

the method. A further advantage of using vermiculite is the very small amount of carbon dioxide evolved in the

blank vessels (nearly zero), because of the low level of microbial activity. This permits low levels of degradation

activity to be evaluated precisely.

The mineralization rates obtained with the activated vermiculite are identical, or very similar, to those obtained

with mature compost, both in terms of the final degradation level and the degradation rate.

5 Test environment

Incubation shall be in the dark or in diffused light, in an enclosure or room maintained at a constant temperature

of 58 °C ± 2 °C and free from vapours inhibitory to microorganisms.

In special cases, e.g. when the melting point of the test material is low, another temperature may be chosen.

This temperature shall be kept constant during the test to within ±2 °C. Any change in temperature shall be

justified and clearly indicated in the test report.
6 Reagents
6.1 TLC (thin-layer chromatography) grade cellulose

Use TLC (thin-layer chromatography) grade cellulose with a particle size of less than 20 µm as the positive-

control reference material.
6.2 Vermiculite

Vermiculite is a clay mineral used for building purposes, known to be particularly suitable as a microbial carrier,

allowing survival and full activity of microbes. The composition of the native mineral, before heat treatment, is

Al O 10 %, MgO 30 %, CaO 5 %, SiO 50 % and combined H O 5 %. When the mineral is subjected to heat

2 3 2 2

treatment, it loses the combined water and expands, giving “expanded vermiculite”. Expanded vermiculite in

flake form shall be used. Expanded vermiculite has a large capacity for water storage, and a water content

comparable with that of mature compost can be obtained in the bed.
© ISO 2012 – All rights reserved 3
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SIST EN ISO 14855-1:2013
ISO 14855-1:2012(E)
Vermiculite can be classified into three types, as follows:
3 3

“Concrete” type: apparent density 80 kg/m ± 16 kg/m (at the time the material is put into sacks); particle size:

80 % between 12 mm and 4 mm, 2 % passing through a 0,5 mm sieve.
3 3

“Medium” type: apparent density 90 kg/m ± 16 kg/m ; particle size: 80 % between 6 mm and 1 mm, 2 %

passing through a 0,5 mm sieve.
3 3

“Fine” type: apparent density 100 kg/m ± 20 kg/m ; particle size: 80 % between 3 mm and 0,7 mm, 5 %

passing through a 0,5 mm sieve.
For the purposes of this part of ISO 14855, the concrete type is used.
7 Apparatus

Ensure that all glassware is thoroughly cleaned and, in particular, free from organic or toxic matter.

7.1 Composting vessels: Glass flasks or bottles that allow an even gas purge in an upward direction.

A minimum volume of 2 litres is required to meet the requirements specified in 8.2 and 8.3. Depending on the

test material, a smaller volume may be used for screening purposes. If the loss in mass of the test material is

to be determined, weigh each composting vessel empty.

7.2 Air-supply system, capable of supplying each composting vessel with dry or water-saturated, if required

carbon-dioxide-free, air at a pre-set flow rate which shall be high enough to provide truly aerobic conditions

during the test (see example given in Annex A).

7.3 Apparatus for the determination of carbon dioxide, designed to determine carbon dioxide directly or by

complete absorption in a basic solution and determination of the dissolved inorganic carbon (DIC) (see example

given in Annex A). If the carbon dioxide in the exhaust air is measured directly, for example with a continuous

infrared analyser or a gas chromatograph, exact control or measurement of the air-flow rate is required.

7.4 Gas-tight tubes, to connect the composting vessels with the air supply and the carbon dioxide

measurement system.
7.5 pH-meter.

7.6 Analytical equipment, for the determination of dry solids (at 105 °C), volatile solids (at 550 °C) and

total organic carbon (TOC), for elemental analysis of the test material and, if required, for the determination of

dissolved inorganic carbon (DIC).

7.7 Balance (optional), to measure the mass of test vessels containing compost and test material, which is

normally in the range between 3 kg and 5 kg.

7.8 Analytical equipment (optional), for the determination of oxygen in the air, moisture, volatile fatty acids

and total nitrogen (e.g. by the Kjeldahl method as specified in ISO 5663).

7.9 Bioreactors for activation of the vermiculite: Containers, with a volume between 5 l and 20 l, which

are not actively aerated. The containers shall be closed in such a way as to avoid excessive drying out of the

contents. Openings shall, however, be provided to allow gas exchange with the atmosphere and ensure aerobic

conditions throughout the activation phase.

An example of a suitable bioreactor is a box, made of polypropylene or another suitable material, having the

following dimensions: 30 cm × 20 cm × 10 cm (l, w, h). The box shall have a tightly fitting lid in order to avoid

excessive loss of water vapour. In the middle of the two 20-cm-wide sides, a hole 5 mm in diameter shall be

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SIST EN ISO 14855-1:2013
ISO 14855-1:2012(E)

made at a height of about 6,5 cm from the bottom of the box. It is these two holes which allow gas exchange

between the atmosphere inside the box and the outside environment.
8 Procedure
8.1 Preparation of the inoculum

Well aerated compost from a properly operating aerobic composting plant shall be used as the inoculum. The

inoculum shall be homogeneous and free from large inert objects such as glass, stones or pieces of metal.

Remove them manually and then sieve the compost on a screen of about 0,5 cm to 1 cm.

NOTE 1 It is recommended that compost from a plant composting the organic fraction of solid municipal waste be used

in order to ensure sufficient diversity of microorganisms. The age of the compost should preferably be between 2 and 4

months. If such compost is not available, compost from plants treating garden or farmyard waste or mixtures of garden

waste and solid municipal waste may be used.

NOTE 2 It is recommended that compost with sufficient porosity be used to enable aerobic conditions to be maintained

...