EN ISO 14853:2017
Current
The latest, up-to-date edition.
Plastics - Determination of the ultimate anaerobic biodegradation of plastic materials in an aqueous system - Method by measurement of biogas production (ISO 14853:2016)
06-12-2017
European foreword
Foreword
Introduction
1 Scope
2 Normative references
3 Terms and definitions
4 Principle
5 Reagents and materials
6 Apparatus
7 Procedure
8 Calculation and expression of results
9 Validity of results
10 Test report
Annex A (informative) - Example of apparatus
for determining the amount of biogas produced
by measuring the increase in gas pressure
Annex B (informative) - Example of apparatus for
determining volumetrically the amount of
biogas produced
Annex C (informative) - Example of a biodegradation curve
Annex D (informative) - Examples of data sheets for
anaerobic biodegradability tests
Annex E (informative) - Table of water vapour pressures
at various temperatures
Annex F (informative) - Calculation of theoretical carbon
dioxide (ThCO[2]) and theoretical methane (ThCH[4])
production
Annex G (informative) - Example of determination of recovery rate
Annex H (informative) - Example of a workflow scheme
Bibliography
ISO 14853:2016 specifies a method for the determination of the ultimate anaerobic biodegradability of plastics by anaerobic microorganisms. The conditions described in ISO 14853 do not necessarily correspond to the optimum conditions for the maximum degree of biodegradation to occur. The test calls for exposure of the test material to sludge for a period of up to 90 d, which is longer than the normal sludge retention time (25 to 30 d) in anaerobic digesters, although digesters at industrial sites can have much longer retention times.The method applies to the following materials:- natural and/or synthetic polymers, copolymers or mixtures thereof;- plastic materials which contain additives such as plasticizers, colorants or other compounds;- water-soluble polymers;- materials which, under the test conditions, do not inhibit the microorganisms present in the inoculum. Inhibitory effects can be determined using an inhibition control or by another appropriate method (see e.g. ISO 13641). If the test material is inhibitory to the inoculum, a lower test concentration, another inoculum or a pre-exposed inoculum can be used.
Committee |
CEN/TC 249
|
DocumentType |
Standard
|
PublisherName |
Comite Europeen de Normalisation
|
Status |
Current
|
Standards | Relationship |
ISO 14853:2016 | Identical |
NEN EN ISO 14853 : 2018 | Identical |
DIN EN ISO 14853 E : 2018 | Identical |
SN EN ISO 14853 : 2018 | Identical |
UNI EN ISO 14853 : 2018 | Identical |
ONORM EN ISO 14853 : 2018 | Identical |
I.S. EN ISO 14853:2017 | Identical |
NS EN ISO 14853 : 2017 | Identical |
PN EN ISO 14853 : 2018 | Identical |
DIN EN ISO 14853:2018-02 | Identical |
BS EN ISO 14853:2017 | Identical |
UNE-EN ISO 14853:2018 | Identical |
NF EN ISO 14853 : 2017 | Identical |
SS-EN ISO 14853 : 2018 | Identical |
ISO 11923:1997 | Water quality — Determination of suspended solids by filtration through glass-fibre filters |
ISO 11734:1995 | Water quality — Evaluation of the "ultimate" anaerobic biodegradability of organic compounds in digested sludge — Method by measurement of the biogas production |
ISO 8245:1999 | Water quality Guidelines for the determination of total organic carbon (TOC) and dissolved organic carbon (DOC) |
ISO 7827:2010 | Water quality Evaluation of the "ready", "ultimate" aerobic biodegradability of organic compounds in an aqueous medium Method by analysis of dissolved organic carbon (DOC) |
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