1、September 2014Translation by DIN-Sprachendienst.English price group 15No part of this translation may be reproduced without prior permission ofDIN Deutsches Institut fr Normung e. V., Berlin. Beuth Verlag GmbH, 10772 Berlin, Germany,has the exclusive right of sale for German Standards (DIN-Normen).I
2、CS 13.060.45!%:H“2239637www.din.deDDIN EN 16479Water quality Performance requirements and conformity test procedures for watermonitoring equipment Automated sampling devices (samplers) for water and waste water;English version EN 16479:2014,English translation of DIN EN 16479:2014-09Wasserbeschaffen
3、heit Leistungsanforderungen und Konformittsprfungen fr Gerte zum Wassermonitoring Automatische Probenahmegerte fr Wasser und Abwasser;Englische Fassung EN 16479:2014,Englische bersetzung von DIN EN 16479:2014-09Qualit de leau Exigences de performance et modes opratoires dessai de conformit pour lesq
4、uipements de surveillance de leau Dispositifs dchantillonnage automatiques (chantillonneurs) pour leau et les eauxuses;Version anglaise EN 16479:2014,Traduction anglaise de DIN EN 16479:2014-09www.beuth.deIn case of doubt, the German-language original shall be considered authoritative.Document compr
5、ises 33 pages08.14 DIN EN 16479:2014-092 A comma is used as the decimal marker. National foreword This document (EN 16479-1:2014) has been prepared by Technical Committee CEN/TC 230 “Water analysis” (Secretariat: DIN, Germany). The responsible German body involved in its preparation was the Normenau
6、sschuss Wasserwesen (DIN Standards Committee Water Practice), Working Committee NA 119-01-03-01-01 AK Probenahme of NA 119-01-03 AA Wasseruntersuchung. EN 16479July 2014 ICS 13.060.45 English Version Water quality - Performance requirements and conformity test procedures for water monitoring equipme
7、nt - Automated sampling devices (samplers) for water and waste water Qualit de leau - Exigences de performance et modes opratoires dessai de conformit pour les quipements de surveillance de leau - Dispositifs dchantillonnage automatiques (chantillonneurs) pour leau et les eaux uses Wasserbeschaffenh
8、eit - Leistungsanforderungen und Konformittsprfungen fr Gerte zum Wassermonitoring - Automatische Probenahmegerte fr Wasser und Abwasser This European Standard was approved by CEN on 22 May 2014. CEN members are bound to comply with the CEN/CENELEC Internal Regulations which stipulate the conditions
9、 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 t
10、hree 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
11、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
12、, Spain, Sweden, Switzerland, Turkey andUnited Kingdom. CEN-CENELEC Management Centre: Avenue Marnix 17, B-1000 Brussels 2014 CEN All rights of exploitation in any form and by any means reserved worldwide for CEN national Members. Ref. No. EN 16479:2014 EEUROPEAN COMMITTEE FOR STANDARDIZATIONCOMIT E
13、UROPEN DE NORMALISATIONEUROPISCHES KOMITEE FR NORMUNGEUROPEAN STANDARDNORME EUROPENNEEUROPISCHE NORMEN 16479:2014 (E) 2 Contents Page Foreword . 3 Introduction 4 1 Scope 5 2 Normative References 5 3 Terms and definitions . 5 4 General requirements for samplers 7 5 Performance requirements 9 5.1 Samp
14、le volume 9 5.2 Sampling principles 9 5.3 Sample line velocity 10 5.4 Power supply . 10 5.5 Sample integrity 10 5.6 Sample timing error 10 5.7 Effect of ambient air temperature 10 6 Conformity testing 11 6.1 General requirements . 11 6.2 Test conditions 11 6.3 Verification by inspection 12 6.4 Perfo
15、rmance tests . 12 Annex A (normative) Evaluation of conformity test data 19 A.1 Sample volume error 19 A.2 Sample line velocity 21 A.3 Sample integrity 21 A.3.1 Calculation of results based on the analysis of variance . 21 A.3.2 Notation 21 A.3.3 Calculations . 22 A.3.4 Interpretation of the results
16、 . 23 A.4 Sampler timing error . 25 A.5 Ambient air temperature effects 25 Annex B (informative) Example procedure for demonstrating sample integrity for samplers to be used for Urban Waste Water Treatment Directive (UWWTD) sampling 27 B.1 General . 27 B.2 Test fluid 27 B.3 Sample collection 27 B.4
17、Sample volume 28 B.5 Sample integrity 28 B.6 Determination of conformance 28 Annex C (informative) Example format for the report 29 Bibliography . 31 DIN EN 16479:2014-09EN 16479:2014 (E) 3 Foreword This document (EN 16479:2014) has been prepared by Technical Committee CEN/TC 230 “Water analysis”, t
18、he secretariat of which is 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 January 2015, and conflicting national standards shall be withdrawn at the latest by January 2015. Attention
19、 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 was submitted to the Formal Vote with the reference FprEN 16479-1. According to t
20、he CEN-CENELEC Internal Regulations, the national standards organizations 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,
21、Hungary, Iceland, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta, Netherlands, Norway, Poland, Portugal, Romania, Slovakia, Slovenia, Spain, Sweden, Switzerland, Turkey and the United Kingdom. DIN EN 16479:2014-09EN 16479:2014 (E) 4 Introduction This European Standard is a product standard for
22、 automated sampling devices (samplers) for water and waste water. It defines general requirements, performance requirements, and procedures for the conformity testing of samplers. Samplers that are shown, by means of the tests, to conform with the specified requirements are considered to be fit for
23、purpose. However, this European Standard does not cover the installation and on-going use of samplers. The requirements of this European Standard are intended to be independent of measurement technology and applicable to all automated sampling devices. Water monitoring equipment is widely used for c
24、ompliance monitoring purposes under national and European regulations. This European standard supports the requirements of the following EU Directives: Industrial Emissions Directive (2010/75/EU) 6. Urban Waste Water Treatment Directive (UWWTD) (91/271/EEC and 98/15/EEC) 7. Water Framework Directive
25、 (2000/60/EC) 8. Marine Strategy Framework Directive (2008/56/EC) 9. DIN EN 16479:2014-09EN 16479:2014 (E) 5 1 Scope This European Standard defines general requirements, performance requirements and conformity test procedures for automated sampling devices (samplers) for water and waste water that:
26、sample water and waste water from non-pressurized (i. e. open to atmosphere) channels or vessels; sample over extended periods to collect discrete or composite samples based on time, event or flow proportional sampling. Specific sample integrity requirements are defined for samplers to be used for t
27、he collection of samples of final effluent or influent for the purpose of monitoring the performance of waste water treatment works, as required under the Urban Waste Water Treatment Directive (UWWTD). Samplers to be used for other industrial applications do not have to be assessed against these spe
28、cific sample integrity requirements. This European Standard does not cover the installation and on-going use of samplers. 2 Normative References The following documents, in whole or in part, are normatively referenced in this document and are indispensable for its application. For dated references,
29、only the edition cited applies. For undated references, the latest edition of the referenced document (including any amendments) applies. EN ISO 5667-3:2012, Water quality - Sampling - Part 3: Preservation and handling of water samples (ISO 5667-3:2012) EN ISO/IEC 17025, General requirements for the
30、 competence of testing and calibration laboratories (ISO/IEC 17025) 3 Terms and definitions For the purposes of this document, the following terms and definitions apply. 3.1 automated sampling device for water and waste water automated sampler equipment for collecting and storing samples of water or
31、 waste water for subsequent analysis 3.2 bias estimate of a systematic measurement error Note 1 to entry: The systematic measurement error is a component of measurement error that in replicate measurements remains constant or varies in a predictable manner. SOURCE: ISO/IEC Guide 99:2007, 2.18, modif
32、ied Note 1 to entry has been added. 3.3 composite sample two or more samples or sub-samples, mixed together in appropriate known proportions (either discretely or continuously), from which the average result of a desired requirement may be obtained Note 1 to entry: The proportions are usually based
33、on time or flow measurements. SOURCE: ISO 6107-2:2006/AMD, 1:2012, 29 DIN EN 16479:2014-09EN 16479:2014 (E) 6 3.4 constant volume variable time sampling C.V.V.T flow proportional sampling based on collecting equal volumes of sample at frequencies proportional to flow 3.5 constant time variable volum
34、e sampling C.T.V.V flow proportional sampling based on collecting samples at fixed time intervals but where the volume of sample is varied in proportion to the flow 3.6 constant time constant volume sampling C.T.C.V equal volumes of sample or sub-sample collected at equal increments of time 3.7 dete
35、rminand property/substance that is required to be measured and to be reflected by/present in a calibration solution SOURCE: EN ISO 15839:2006, 3.13 3.8 discrete sample single sample taken from a body of water SOURCE: ISO 6107-2:2006, 40, modified “process, whereby” deleted 3.9 measurement error erro
36、r of measurement error measured quantity value minus a reference quantity value Note 1 to entry: The concept of “measurement error” can be used both: a) when there is a single reference quantity value to refer to, which occurs if a calibration is made by means of a measurement standard with a measur
37、ed quantity value having a negligible measurement uncertainty or if a conventional quantity value is given, in which case the measurement error is known, and b) if a measurand is supposed to be represented by a unique true quantity value or a set of true quantity values of negligible range, in which
38、 case the measurement error is not known. Note 2 to entry: Measurement error is not be confused with production error or mistake. SOURCE: ISO/IEC Guide 99:2007, 2.16 3.10 rated operating conditions minimum to maximum values of any environmental, fluid or electrical parameter within which the sampler
39、 is designed to operate without adjustment and with errors within performance limits 3.11 lift height vertical distance between the surface of the fluid being sampled and the highest point to which the sample is lifted Note 1 to entry: Sometimes called “sampling head” or “suction height”. DIN EN 164
40、79:2014-09EN 16479:2014 (E) 7 Note 2 to entry: The maximum lift height for samplers using vacuum pumps (e.g. pneumatic samplers and peristaltic samplers) is set to an atmospheric pressure of 1 000 mbar. At low atmospheric pressure the maximum lift height will be consequentially lower. 3.12 precision
41、 closeness of agreement between indications or measured quantity values obtained by replicate measurements on the same or similar objects under specified conditions Note 1 to entry: Measurement precision is usually expressed numerically by measures of imprecision, such as standard deviation, varianc
42、e, or coefficient of variation under specified conditions of measurement. Note 2 to entry: The “specified conditions” can be, for example, repeatability conditions of measurement, intermediate precision conditions of measurement, or reproducibility conditions of measurement (see ISO 5725-3:1994). No
43、te 3 to entry: Measurement precision is used to define measurement repeatability, intermediate measurement precision, and measurement reproducibility. Note 4 to entry: Sometimes “measurement precision” is erroneously used to mean measurement accuracy. SOURCE: ISO/IEC Guide 99:2007, 2.15 3.13 samplin
44、g interval time between successive sampling events 3.14 sampling line conduit from intake point to inlet of dosing system SOURCE: ISO 6107-2:2006/AMD, 1:2012, 115, modified “sampling probe” was replaced by “intake point” and delivery point was replaced by “inlet of dosing system” 4 General requireme
45、nts for samplers See 6.3 for details on verification by inspection. A sampler shall: a) have an unique designation that unambiguously identifies it (e.g. model, serial number); b) be designed (including its operating methodology) and constructed to ensure that the composition of the sample is, as fa
46、r as is practicable, not altered by the sampling procedure; It can be impracticable to prevent the loss of volatile substances during sampling with vacuum and peristaltic samplers. c) have a rated maximum lift height at which all of the performance requirements of this standard are fulfilled. The ra
47、ted maximum lift height shall be inscribed on the sampler or declared in the operating manual published by the manufacturer; Conformity testing of the sampler shall be based on a range of lift heights up to and including the samplers rated maximum lift height. d) have provision for the user to set t
48、he volume of a discrete sample; e) have rated minimum and maximum sample volumes of a discrete sample inscribed on the sampler or declared in the operating manual published by the manufacturer; DIN EN 16479:2014-09EN 16479:2014 (E) 8 Unless otherwise stated conformity testing of the sampler shall be
49、 based on a sample volume of 250 ml or the rated maximum sample volume, if smaller. f) have the stated capacities, for any integrated sample storage, both by number(s) and volume(s) of individual bottles and of a composite container, inscribed on the sampler or declared in the operating manual published by the manufacturer; g) be capable of collecting a series of samples, on a timed, event and/or a flow proportional bas
