SIST EN 13592:2003+A1:2008
(Main)Plastics sacks for household waste collection - Types, requirements and test methods
Plastics sacks for household waste collection - Types, requirements and test methods
This European Standard specifies the general characteristics, test methods and requirements for sacks made from plastics films, used for household waste pre-collection, household waste collection, or household selective waste collection.
Kunststoffsäcke für die Abfallsammlung aus Haushalten - Typen, Anforderungen und Prüfverfahren
Diese Norm legt die allgemeinen Merkmale, Prüfverfahren und Anforderungen für Säcke aus Kunststoff-Folien fest, die für die vorläufige Sammlung, die Sammlung oder die getrennte Sammlung von Haushaltsabfällen verwendet werden.
Sacs en plastique pour la collecte des déchets ménagers - Types, exigences et méthodes d'essai
La présente norme spécifie les caractéristiques générales, les méthodes d'essai et les exigences relatives aux sacs faits de films plastiques, utilisés pour la précollecte, la collecte ou la collecte sélective des déchets ménagers.
Plastične vreče za zbiranje gospodinjskih odpadkov - Vrste, zahteve in preskusne metode (vključno z dopolnilom A1)
General Information
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Standards Content (Sample)
2003-01.Slovenski inštitut za standardizacijo. Razmnoževanje celote ali delov tega standarda ni dovoljeno.Kunststoffsäcke für die Abfallsammlung aus Haushalten - Typen, Anforderungen und PrüfverfahrenSacs en plastique pour la collecte des déchets ménagers - Types, exigences et méthodes d'essaiPlastics sacks for household waste collection - Types, requirements and test methods55.080Sacks. Bags13.030.40Naprave in oprema za odstranjevanje in obdelavo odpadkovInstallations and equipment for waste disposal and treatmentICS:Ta slovenski standard je istoveten z:EN 13592:2003+A1:2007SIST EN 13592:2003+A1:2008en,fr,de01-januar-2008SIST EN 13592:2003+A1:2008SLOVENSKI
STANDARDSIST EN 13592:2003/AC:2005SIST EN 13592:20031DGRPHãþD
SIST EN 13592:2003+A1:2008
EUROPEAN STANDARD NORME EUROPÉENNE EUROPÄISCHE NORM
EN 13592:2003+A1
July 2007 ICS 13.030.40; 55.080 Supersedes EN 13592:2003 English Version
Plastics sacks for household waste collection - Types, requirements and test methods
Sacs en plastique pour la collecte des déchets ménagers -Types, exigences et méthodes d'essai
Kunststoffsäcke für die Abfallsammlung aus Haushalten - Typen, Anforderungen und Prüfverfahren This European Standard was approved by CEN on 6 December 2002 and includes Amendment 1 approved by CEN on 22 June 2007 and the Corrigendum issued in 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 CEN 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 Management Centre has the same status as the official versions.
CEN members are the national standards bodies of Austria, Belgium, Bulgaria, 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 © 2007 CEN All rights of exploitation in any form and by any means reserved worldwide for CEN national Members. Ref. No. EN 13592:2003+A1:2007: ESIST EN 13592:2003+A1:2008
EN 13592:2003+A1:2007 (E) 2 Contents page Foreword.3 Introduction.4 1 Scope.4 2 Normative references.4 3 Terms and definitions.5 4 Designation.6 5 Dimensions.6 6 Requirements.7 7 Sampling.9 8 Conditioning for testing.9 9 Test methods.9 10 Marking.20 Annex A (informative)
Types of sacks.21 Annex B (normative)
Sampling.22 Bibliography.23
SIST EN 13592:2003+A1:2008
EN 13592:2003+A1:2007 (E) 3 Foreword This document (EN 13592:2003+A1:2007) has been prepared by Technical Committee CEN/TC 261 "Packaging", the secretariat of which is held by AFNOR. This document shall be given the status of a national standard, either by publication of an identical text or by endorsement, at the latest by January 2008 and conflicting national standards shall be withdrawn at the latest by January 2008. This document includes Amendment 1 approved by CEN on 2007-06-22 and the Corrigendum issued in 2005. This document supersedes EN 13592:2003. The start and finish of text introduced or altered by amendment is indicated in the text by tags ! ". The modifications of the related CEN Corrigendum have been implemented at the appropriate places in the text and are indicated by the tags ˜™. Annex A is informative. Annex B is normative. According to the CEN/CENELEC Internal Regulations, the national standards organizations of the following countries are bound to implement this European Standard: Austria, Belgium, Bulgaria, 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. SIST EN 13592:2003+A1:2008
EN 13592:2003+A1:2007 (E) 4 Introduction In many European countries, the collection of household waste is part of a waste management system, which means that households have to separate out waste according to the final method of disposal. This European Standard is based on the existing national standards for plastics sacks for waste collection available at the date of issue which are listed in the bibliograhy. 1 Scope This European Standard specifies the general characteristics, test methods and requirements for sacks made from plastics films, used for household waste pre-collection, household waste collection, or household selective waste collection. 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 22248, Packaging – Complete, filled transport packages – Vertical impact test by dropping (ISO 2248:1985). EN ISO 527-3, Plastics – Determination of tensile properties – Part 3: Test conditions for films and sheets (ISO 527-3:1995). EN ISO 7965-2, Sacks – Drop test – Part 2: Sacks made from thermoplastic flexible film (ISO 7965-2:1993). ISO 1043-1, Plastics – Symbols and abbreviated terms – Part 1: Basic polymers and their special characteristics. ISO 4593, Plastics – Film and sheeting – Determination of thickness by mechanical scanning. SIST EN 13592:2003+A1:2008
EN 13592:2003+A1:2007 (E) 5 3 Terms and definitions For the purposes of this European Standard, the following terms and definitions apply. 3.1
standard sack open mouthed sack 3.2
sack for selective waste collection SWC sack used for collection of some flows of waste, separated beforehand by producers with the view of valorisation or specific treatment 3.3
tie any item incorporated by design or added, used to close the sack NOTE Examples include: polypropylene tape, clips and wire ties 3.4
drawtight sack sack with a tie inserted in the top of the sack, allowing it to be closed and, in some cases, be carried 3.5
four flap sack sack with four flaps used for closure by knotting 3.6
strapsack sack with two straps used as ties for closure and as handles to carry the sack 3.7
household waste non dangerous waste from household or from industrial activities or service activities, collected in the same conditions NOTE To prevent damage to the sack, unwrapped broken glass and unwrapped sharp edges are not normally placed in them. 3.8
gusset fold or series of folds inserted in the longitudinal edge of the sack 3.9
useful length, L distance from the bottom to the mouth of the sack, measured inside the sack lying flat (see 9.1.2) 3.10 useful width, P internal width of the sack, measured with gussets unfolded, if any (see 9.1.3) 3.11
nominal thickness, Nt
thickness of the film, as declared by the manufacturer or agreed upon in the contract, in micrometres, (µm) (see 9.1.4) SIST EN 13592:2003+A1:2008
EN 13592:2003+A1:2007 (E) 6 4 Designation Sacks are designated using the following information: a) end use, i.e. household waste collection sacks, household waste selective collection sacks with their specific test loads, agreement if any between supplier and buyer according to 6.5.2 and/or 6.6.3, and if necessary any other information agreed between the supplier and buyer; b) the dimensions, in millimetres (mm); c) the type:
standard sacks,
drawtight sacks,
strap sacks,
four flap sacks, NOTE 1 The above list of types is neither restrictive nor exhaustive. Annex A shows these different types of sacks. d) the symbol of the plastic material used, in accordance with ISO 1043-1, and its colour; e) the nominal thickness, in micrometres (µm); f) a reference to this European Standard i.e EN 13592. NOTE 2 Colour is a basic information used for the designation of the sack, e.g., black, blue, green, white. When no pigment, load or coloured master batch is incorporated in the resin, it is specified as “neutral”. When a more accurate definition of colour is needed, it should be specified in the contract, with reference to the relevant specification or standard. Examples of designation: 1) for household waste collection sack, 700 mm x 1 100 mm, standard, in polyethylene, white, 40 µm thick: "Household waste collection sack - EN 13952 - 700/1100 - Standard - PE - White - 40 µm " 2) for household selective waste collection drawtight sack, 600 mm x 800 mm, in polyethylene, neutral, 30 µm thick for specific load of 4 kg both for drop test and closing device test: "Household selective waste collection sack for 4 kg
- EN 13592 - 600/800 - Drawtight - PE - Neutral - 30 µm “ Other information could be added under agreement between supplier and buyer. 5 Dimensions The dimensions of the sack shall be agreed between supplier and buyer. The different dimensions of sacks are given by two separate numbers in millimetres, the first specifying the useful width (see 3.10 and 9.1.3) and the second the useful length of the sack (see 3.9 and 9.1.2). Table 1 gives examples of sack dimensions. SIST EN 13592:2003+A1:2008
EN 13592:2003+A1:2007 (E) 7 Table 1 — Examples of sack dimensions Reference
Useful width, P, in mm
Useful length, L, in mm 400×450 400 450 500×700 500 700 700×1100 700 1 100
6 Requirements 6.1 Useful width and useful length The minimum useful width measured shall not be less than: P - 2,5 %. The minimum useful length measured shall not be less than: L - 2,5 %. No defective sacks shall be permitted out of 10 sacks tested according to 9.1.3.
6.2 Film thickness 6.2.1 Individual values for thickness No defective sack shall be permitted out of 10 sacks (or strips) tested according to 9.1.4 for individual values of each sack (or strip) and the overall average value of the 10 measurements.
6.2.2 Individual values No individual thickness measured in micrometres (µm), according to 9.1.4 shall be less than Nt - x where
X = tt
25 15NN+ rounded to the nearest upper or lower unit (µm) (1,4 as 1 µm; 1,5 as 2 µm; 1,6 as 2µm)
6.2.3 Average value The arithmetic average value of the measurements made in accordance with 9.1.4 shall be: a) greater than Nt – 5 %, when Nt is greater than 20 micrometres. b) greater than Nt – 8 %, when Nt is less or equal to 20 micrometres.
SIST EN 13592:2003+A1:2008
EN 13592:2003+A1:2007 (E) 8 6.3 Opacity 6.3.1 General Unless otherwise specified the level of opacity, as measured in accordance with 9.2, shall be: - greater than or equal to 60 % for household waste collection sacks; - less than or equal to 40 % for household selective waste collection sacks. No defective sack shall be permitted out of 10 sacks (or strips) tested according to 9.2 for individual values of each sack (or strip) and the overall value of the 10 measurements.
6.3.2 Individual values No individual opacity measured in % according to 9.2 shall be: a) less than or equal to (60 – 5 = 55) % for household waste collection sacks; b) greater than or equal to (40 + 5 = 45) % for household selective waste collection sacks.
6.3.3 Average value The arithmetic average value of the measurements made in accordance with 9.2 shall be: a) greater than or equal to 60 % for household waste collection sacks; b) less than or equal to 40 % for household selective waste collection sacks.
6.4 Resistance to leakage No defective sack shall be permitted out of 5 sacks tested according to 9.3.
6.5 Drop impact resistance 6.5.1 Sacks for household waste collection Not more than 3 defective sacks shall be permitted out of 30 sacks tested according to 9.4.
6.5.2 Sacks for selective waste collection For these sacks there can be a specific agreement between supplier and buyer for different test loads (see 9.4.2.2). Without any specific agreement test loads according to Table 3 of 9.4.2.2 apply. In any case, not more than
3 defective sacks shall be permitted out of 30 sacks tested according to 9.4.
SIST EN 13592:2003+A1:2008
EN 13592:2003+A1:2007 (E) 9 6.6 Resistance of the closing device 6.6.1 Tensile strength of the tie In the case of sacks provided with an incorporated or added tie, the tensile strength measured according to 9.5.1 shall not be less than 40 N. Not more than one failure out of 10 ties tested is permitted. When the tie is not integral with the sack, the number of ties shall not be less than the number of sacks.
6.6.2 Resistance of the closing device of drawtight sacks Not more than 1 defective sack out of 10 is permitted when tested according to 9.5.2
6.6.3 Resistance of closing device of drawtight sacks for selective waste collection For these sacks, if there is a
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