BS-EN-ISO-15181-1-2007.pdf

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1、BRITISH STANDARD BS EN ISO 15181-1:2007 Paints and varnishes Determination of release rate of biocides from antifouling paints Part 1: General method for extraction of biocides The European Standard EN ISO 15181-1:2007 has the status of a British Standard ICS 87.040 ? BS EN ISO 15181-1:2007 This Bri

2、tish Standard was published under the authority of the Standards Policy and Strategy Committee on 28 September 2007 BSI 2007 ISBN 978 0 580 55942 6 National foreword This British Standard is the UK implementation of EN ISO 15181-1:2007. It supersedes BS EN ISO 15181-1:2004 which is withdrawn. The UK

3、 participation in its preparation was entrusted to Technical Committee STI/10, Test methods for paints. A list of organizations represented on this committee can be obtained on request to its secretary. This publication does not purport to include all the necessary provisions of a contract. Users ar

4、e responsible for its correct application. Compliance with a British Standard cannot confer immunity from legal obligations. Amendments issued since publication Amd. No. DateComments EUROPEAN STANDARD NORME EUROPENNE EUROPISCHE NORM EN ISO 15181-1 June 2007 ICS 87.040Supersedes EN ISO 15181-1:2004 E

5、nglish Version Paints and varnishes - Determination of release rate of biocides from antifouling paints - Part 1: General method for extraction of biocides (ISO 15181-1:2007) Peintures et vernis - Dtermination du taux de lixiviation des biocides contenus dans les peintures antisalissures - Partie 1:

6、 Mthode gnrale dextraction des biocides (ISO 15181-1:2007) Beschichtungsstoffe - Bestimmung der Auswaschrate von Bioziden aus Antifouling-Beschichtungen - Teil 1: Allgemeines Verfahren zur Extraktion von Bioziden (ISO 15181-1:2007) This European Standard was approved by CEN on 16 May 2007. CEN membe

7、rs 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 applicatio

8、n 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 th

9、e 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, Portug

10、al, Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland and United Kingdom. EUROPEAN COMMITTEE FOR STANDARDIZATION COMIT EUROPEN DE NORMALISATION EUROPISCHES KOMITEE FR NORMUNG Management Centre: rue de Stassart, 36 B-1050 Brussels 2007 CENAll rights of exploitation in any form and by any means

11、reserved worldwide for CEN national Members. Ref. No. EN ISO 15181-1:2007: E Foreword This document (EN ISO 15181-1:2007) has been prepared by Technical Committee ISO/TC 35 “Paints and varnishes“ in collaboration with Technical Committee CEN/TC 139 “Paints and varnishes“, the secretariat of which is

12、 held by DIN. 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 December 2007, and conflicting national standards shall be withdrawn at the latest by December 2007. This document supersedes EN ISO 1

13、5181-1:2004. 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, Ire

14、land, Italy, Latvia, Lithuania, Luxembourg, Malta, Netherlands, Norway, Poland, Portugal, Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland and United Kingdom. Endorsement notice The text of ISO 15181-1:2007 has been approved by CEN as EN ISO 15181-1:2007 without any modifications. EN ISO 1518

15、1-1:2007 Reference number ISO 15181-1:2007(E) INTERNATIONAL STANDARD ISO 15181-1 Second edition 2007-06-01 Paints and varnishes Determination of release rate of biocides from antifouling paints Part 1: General method for extraction of biocides Peintures et vernis Dtermination du taux de lixiviation

16、des biocides contenus dans les peintures antisalissures Partie 1: Mthode gnrale dextraction des biocides EN ISO 15181-1:2007 ii iii Contents Page Foreword iv Introduction v 1 Scope . 1 2 Normative references. 1 3 Principle. 2 4 Required supplementary information. 2 5 Apparatus 2 6 Reagents and mater

17、ials . 4 7 Sampling 5 8 Preparation of test cylinders . 5 9 Procedure 6 10 Extraction method 6 11 Test report . 7 Annex A (normative) Supplementary information 8 Bibliography. 9 EN ISO 15181-1:2007 iv Foreword ISO (the International Organization for Standardization) is a worldwide federation of nati

18、onal 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. Internat

19、ional 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 ru

20、les 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

21、 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 15181-1 was prepared by Technical Committee ISO/

22、TC 35, Paints and varnishes, Subcommittee SC 9, General test methods for paints and varnishes. This second edition cancels and replaces the first edition (ISO 15181-1:2000), which has been technically revised, in particular to extend the use of the general extraction method to the later parts of ISO

23、 15181. ISO 15181 consists of the following parts, under the general title Paints and varnishes Determination of release rate of biocides from antifouling paints: Part 1: General method for extraction of biocides Part 2: Determination of copper-ion concentration in the extract and calculation of the

24、 release rate Part 3: Calculation of the zinc ethylene-bis(dithiocarbamate) (zineb) release rate by determination of the concentration of ethylenethiourea in the extract Part 4: Determination of pyridine-triphenylborane (PTPB) concentration in the extract and calculation of the release rate Part 5:

25、Calculation of the tolylfluanid and dichlofluanid release rate by determination of the concentration of dimethyltolylsulfamide (DMST) and dimethylphenylsulfamide (DMSA) in the extract EN ISO 15181-1:2007 v Introduction By using standard conditions of temperature, salinity and pH at low biocide conce

26、ntrations in the surrounding artificial seawater, a repeatable value of the release rate under the specified laboratory conditions can be determined using the method given in this part of ISO 15181, which can be used for quality assurance and material selection purposes. The actual release rate of b

27、iocides from antifouling paints on ships hulls into the environment will, however, depend on many factors, such as ship operating schedules, length of service, berthing conditions, paint condition, as well as the temperature, salinity, pH, pollutants and biological community in a particular area. Th

28、e results of this test do not reflect environmental biocide release rates for antifouling products and are not suitable for direct use in the process of generating environmental-risk assessments, producing environmental- loading estimates or for establishing release rate limits for regulatory purpos

29、es. In comparison with copper and organotin release rates obtained either by direct or indirect measurements of the copper release rate from ships hulls and from measurements made on panels exposed in harbours, all available data indicate that the results obtained using this generic test method sign

30、ificantly overestimate the release rates of biocides under in-service conditions. Published results demonstrate that the results of this test method are generally higher than direct in situ measurements of copper and organotin release rates from in-service ship hulls by a factor of about 10 or more

31、for several commercial antifouling coatings 1, 2. A similar relationship is expected to be found for other biocides. Realistic estimates of the biocide release rate from a ships hull under in-service conditions can only be obtained from this test method if this difference is taken into account. Wher

32、e the results of this test method are used in the process of generating environmental-risk assessments, producing environmental-loading estimates or for regulatory purposes, it is most strongly recommended that the relationship between laboratory release rates and actual environmental inputs be take

33、n into account to allow a more accurate estimate of the biocide release rate from antifouling coatings under real-life conditions to be obtained. This can be accomplished through the application of appropriate correction factors 2. EN ISO 15181-1:2007 blank 1 Paints and varnishes Determination of re

34、lease rate of biocides from antifouling paints Part 1: General method for extraction of biocides 1 Scope This part of ISO 15181 specifies a general method for extracting biocides from antifouling paint films into artificial seawater under specified laboratory conditions. It is used in conjunction wi

35、th the other parts of ISO 15181 to determine the amounts of specific biocides in the extract, for example copper and/or certain organic biocides, and to enable the release rate of those biocides from the paint film under the specified laboratory conditions to be calculated. 2 Normative references Th

36、e 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 1513, Paints and varnishes Examination and prep

37、aration of samples for testing ISO 2808, Paints and varnishes Determination of film thickness ISO 3696, Water for analytical laboratory use Specification and test methods ISO 15181-2, Paints and varnishes Determination of release rate of biocides from antifouling paints Part 2: Determination of copp

38、er-ion concentration in the extract and calculation of the release rate ISO 15181-3, Paints and varnishes Determination of release rate of biocides from antifouling paints Part 3: Calculation of the zinc ethylene-bis(dithiocarbamate) (zineb) release rate by determination of the concentration of ethy

39、lenethiourea in the extract ISO 15181-4, Paints and varnishes Determination of release rate of biocides from antifouling paints Part 4: Determination of pyridine-triphenylborane (PTPB) concentration in the extract and calculation of the release rate ISO 15181-5, Paints and varnishes Determination of

40、 release rate of biocides from antifouling paints Part 5: Calculation of the tolylfluanid and dichlofluanid release rate by determination of the concentration of dimethyltolylsulfamide (DMST) and dimethylphenylsulfamide (DMSA) in the extract ISO 15528, Paints, varnishes and raw materials for paints

41、and varnishes Sampling ASTM D 1141-98(2003), Standard Practice for the Preparation of Substitute Ocean Water EN ISO 15181-1:2007 2 3 Principle Test cylinders painted with antifouling paint are immersed, together with reference cylinders, in flowing artificial seawater in a holding tank. At specified

42、 time intervals, the cylinders are removed and exposed for a defined period in individual release rate measuring containers containing the same artificial seawater before being replaced in the holding tank. The concentration of the biocide released into the water of the individual release rate measu

43、ring containers is then determined. This operation is repeated at defined time intervals and hence the release rate of the biocide under the specified laboratory conditions can be calculated. 4 Required supplementary information For each application, the items of supplementary information listed in

44、Annex A shall be supplied as appropriate to enable the test method given in this part of ISO 15181 to be carried out. 5 Apparatus NOTE Some biocides have a strong tendency to adsorb onto certain glass or plastic substrates. 5.1 Test cylinder, made of an inert material see Annex A, item A.2 a), havin

45、g a diameter of (64 5) mm and length of (178 15) mm, and closed at both ends so that it is watertight. 5.2 Rotating device, capable of rotating a test cylinder (5.1) in the centre of the release rate measuring container (5.3) such that the rotational speed of the outside of the test cylinder through

46、 the artificial seawater is (60 5) r/min (0,2 0,02) m/s. The device itself shall not be allowed to come into contact with the artificial seawater. 5.3 Release rate measuring container (see Figure 1), made of an inert material see Annex A, item A.2 b), of nominal capacity (2 0,2) litres, 120 mm to 15

47、0 mm in diameter and 170 mm to 210 mm high. The container shall be fitted with three evenly spaced baffles around the inside of the container to prevent swirling during test cylinder rotation. The baffles shall consist of circular rods of diameter 5 mm to 7 mm running from the bottom of the containe

48、r to a level at least above that of the artificial seawater. They shall be fixed in place using an inert adhesive or solvent. There shall be a means of maintaining the container and its contents at (25 1) C. NOTE Placing the container in a thermostatically controlled water bath has been found to be

49、a suitable means of maintaining the temperature at the correct level; alternatively, the test may be performed in a conditioned room at the specified temperature. If the release rate of a highly photosensitive biocide is being determined, then the container shall be protected from natural and artificial visible-light sources. Details of this requirement to protect the container from light are indicated in the part of this st

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