DIN EN ISO 16133-2011 Soil quality - Guidance on the establishment and maintenance of monitoring programmes (ISO 16133 2004) German version EN ISO 16133 2011《土壤质量 监测程序的建立和维护指南(ISO .pdf

1、September 2011 Translation by DIN-Sprachendienst.English price group 17No 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).

2、ICS 13.080.05!$tGh“1813669www.din.deDDIN EN ISO 16133Soil quality Guidance on the establishment and maintenance of monitoringprogrammes (ISO 16133:2004)English translation of DIN EN ISO 16133:2011-09Bodenbeschaffenheit Leitfaden zur Einrichtung und zum Betrieb von Beobachtungsprogrammen(ISO 16133:20

3、04)Englische bersetzung von DIN EN ISO 16133:2011-09Qualit du sol Lignes directrices pour ltablissement et lentretien de programmes de surveillance(ISO 16133:2004)Traduction anglaise de DIN EN ISO 16133:2011-09SupersedesDIN ISO 16133:2006-06www.beuth.deDocument comprises pagesIn case of doubt, the G

4、erman-language original shall be considered authoritative.4208.11 DIN EN ISO 16133:2011-09 2 A comma is used as the decimal marker. National foreword This standard has been prepared by Technical Committee ISO/TC 190 “Soil quality” in collaboration with Technical Committee CEN/TC 345 “Characterizatio

5、n of soils” (Secretariat: NEN, Netherlands). The responsible German body involved in its preparation was the Normenausschuss Wasserwesen (Water Practice Standards Committee), Working Committee NA 119-01-02-03 UA Standortbeurteilung. Expert assistance and specialized laboratories will be recommended

6、to perform the sampling procedures described in this standard. The DIN Standards corresponding to the International Standards referred to in this document are as follows: ISO 10381-1 DIN ISO 10381-1 ISO 10381-2 DIN ISO 10381-2 ISO 10381-3 DIN ISO 10381-3 ISO 10381-4 DIN ISO 10381-4 ISO 10390 DIN ISO

7、 10390 ISO 10693 DIN ISO 10693 ISO 10694 DIN ISO 10694 ISO 11074-1 E DIN ISO 11074 ISO 11074-2 E DIN ISO 11074 ISO 11260 DIN EN ISO 11260 ISO 11265 DIN ISO 11265 ISO 11272 DIN ISO 11272 ISO 11277 DIN ISO 11277 ISO 11465 DIN ISO 11465 ISO 13536 DIN ISO 13536 ISO 13878 DIN ISO 13878 ISO 15903 DIN ISO

8、15903 ISO/IEC 17025 DIN EN ISO/IEC 17025 Amendments This standard differs from DIN ISO 16133:2006-06 as follows: a) normative references have been updated; b) the standard has been editorially revised. Previous editions DIN ISO 16133: 2006-06 DIN EN ISO 16133:2011-09 3 National Annex NA (informative

9、) Bibliography DIN 4220, Pedologic site assessment Designation, classification and deduction of soil parameters (normative and nominal scaling) DIN EN ISO 11260, Soil quality Determination of effective cation exchange capacity and base saturation level using barium chloride solution DIN EN ISO/IEC 1

10、7025, General requirements for the competence of testing and calibration laboratories DIN ISO 10381-1, Soil quality Sampling Part 1: Guidance on the design of sampling programmes DIN ISO 10381-2, Soil quality Sampling Part 2: Guidance on sampling techniques DIN ISO 10381-3, Soil quality Sampling Par

11、t 3: Guidance on safety DIN ISO 10381-4, Soil quality Sampling Part 4: Guidance on the procedure for investigation of natural, near-natural and cultivated sites DIN ISO 10390, Soil quality Determination of pH DIN ISO 10693, Soil quality Determination of carbonate content Volumetric method DIN ISO 10

12、694, Soil quality Determination of organic and total carbon after dry combustion (elementary analysis) E DIN ISO 11074, Soil quality Vocabulary DIN ISO 11265, Soil quality Determination of the specific electrical conductivity DIN ISO 11272, Soil quality Determination of dry bulk density DIN ISO 1127

13、7, Soil quality Determination of particle size distribution in mineral soil material Method by sieving and sedimentation DIN ISO 11465, Soil quality Determination of dry matter and water content on a mass basis Gravimetric method DIN ISO 13536, Soil quality Determination of the potential cation exch

14、ange capacity and exchangeable cations using barium chloride solution buffered at pH 8,1 DIN ISO 13878, Soil quality Determination of total nitrogen content by dry combustion (“elemental analysis”) DIN ISO 15903, Soil quality Format for recording soil and site information BMELF (1994): Bundesweite B

15、odenzustandserhebung im Wald Arbeitsanleitung; Bundesministerium fr Ernhrung, Landwirtschaft und Forsten (Federal Ministry of Food, Agriculture and Forests) Eigenverlag, 158 pp. ad-hoc-AG Boden, Bodenkundliche Kartieranleitung, 5. Auflage, Hannover 2005 DIN EN ISO 16133:2011-09 4 This page is intent

16、ionally blank EUROPEAN STANDARD NORME EUROPENNE EUROPISCHE NORM EN ISO 16133 June 2011 ICS 13.080.01 English Version Soil quality - Guidance on the establishment and maintenance of monitoring programmes (ISO 16133:2004) Qualit du sol - Lignes directrices pour ltablissement et lentretien de programme

17、s de surveillance (ISO 16133:2004) Bodenbeschaffenheit - Leitfaden zur Einrichtung und zum Betrieb von Beobachtungsprogrammen (ISO 16133:2004)This European Standard was approved by CEN on 10 June 2011. CEN members are bound to comply with the CEN/CENELEC Internal Regulations which stipulate the cond

18、itions 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 exist

19、s 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 stan

20、dards bodies of Austria, Belgium, Bulgaria, Croatia, 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

21、United Kingdom. EUROPEAN COMMITTEE FOR STANDARDIZATION COMIT EUROPEN DE NORMALISATION EUROPISCHES KOMITEE FR NORMUNG Management Centre: Avenue Marnix 17, B-1000 Brussels 2011 CEN All rights of exploitation in any form and by any means reserved worldwide for CEN national Members. Ref. No. EN ISO 1613

22、3:2011: EContents DIN EN ISO 16133:2011-09 EN ISO 16133:2011 (E) 2 Page Foreword3 Introduction .4 1 Scope 5 2 Terms and definitions .5 3 Monitoring objectives7 3.1 General7 3.2 Examples of monitoring purposes.8 4 Monitoring programme .8 4.1 General considerations.8 4.2 Elements of a monitoring progr

23、amme.9 4.2.1 Status of the monitoring sites 9 4.2.2 Changes at the monitoring sites9 4.2.3 Interpretation of status and changes.10 4.2.4 Selection of sites .10 4.3 Sampling and measurement.11 4.3.1 General11 4.3.2 Site design and identification.11 4.3.3 Soil and site description .11 4.3.4 Sampling.1

24、1 4.3.5 Field and laboratory measurements11 4.3.6 Specimen banking .11 4.3.7 Time interval between samplings 12 5 Data quality and quantity 12 Annex A (informative) Examples of monitoring programmes 13 Bibliography 37 Foreword The text of ISO 16133:2004 has been prepared by Technical Committee ISO/T

25、C 190 “Soil quality” of the International Organization for Standardization (ISO) and has been taken over as EN ISO 16133:2011 by Technical Committee CEN/TC 345 “Characterization of soils” the secretariat of which is held by NEN. This European Standard shall be given the status of a national standard

26、, either by publication of an identical text or by endorsement, at the latest by December 2011, and conflicting national standards shall be withdrawn at the latest by December 2011. Attention is drawn to the possibility that some of the elements of this document may be the subject of patent rights.

27、CEN and/or CENELEC shall not be held responsible for identifying any or all such patent rights. 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, Croatia, Cypru

28、s, 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 the United Kingdom. Endorsement notice The text of ISO 161

29、33:2004 has been approved by CEN as a EN ISO 16133:2011 without any modification. DIN EN ISO 16133:2011-09 EN ISO 16133:2011 (E) 3 Introduction Monitoring is the process of repetitive observation, for defined purposes, of one or more components of the environment according to pre-arranged schedules

30、in space and time using comparable methods for environmental sensing and data collection (see reference 1 in the Bibliography). Monitoring schemes are used all over the world for a large number of purposes. Soil monitoring, particularly, is a long-term undertaking. The quality and the utility of the

31、 information from the monitoring is to a large degree determined by the choice of monitoring sites and by their maintenance over the years, and by appropriate quality control at all stages of the process. Monitoring associated with industrial (contaminated) sites can involve many specific considerat

32、ions, including legal requirements. The guidance in this International Standard is not designed or intended to cover such situations. DIN EN ISO 16133:2011-09 EN ISO 16133:2011 (E) 4 1 Scope This International Standard gives general guidance on the selection of procedures for the establishment and m

33、aintenance of programmes for long-term monitoring of soil quality. It takes into account the large number of objectives for soil-monitoring programmes. This International Standard is intended to help provide a basis for dialogue between parties which might be involved in a monitoring scheme. Example

34、s of soil-monitoring programmes from several countries are provided in Annex A. 2 Terms and definitions For the purposes of this document, the following terms and definitions apply. 2.1 accumulation increase of the concentration of a substance in soil due to substance input being larger than substan

35、ce output NOTE Adapted from ISO 11074-1:1996 2.2 anthropogenic influence changes in soil properties caused by human activities ISO 11074-1:1996 2.3 background concentration natural pedogeochemical content geogeneous or pedogeneous average concentration of a substance in an examined soil ISO 11074-1:

36、1996 2.4 diffuse source input non-point source input input of a substance emitted from moving sources, from sources with a large area or from many sources NOTE 1 The sources can be cars, application of substances through agricultural practices, emissions from town or region, deposition of sediment t

37、hrough flooding of a river. NOTE 2 Diffuse source input usually leads to sites that are relatively uniformly contaminated. At some sites, the input conditions may nevertheless cause a higher local input near the source or where atmospheric deposition/rain is increased. ISO 11074-1:1996 DIN EN ISO 16

38、133:2011-09 EN ISO 16133:2011 (E) 5 2.5 leaching movement of dissolved substances caused by the movement of water or other liquids in the soil ISO 11074-1:1996 2.6 locally contaminated site site with discrete areas of high concentrations of substances hazardous to soil NOTE The extent of contaminati

39、on is usually small and the gradient of concentration within the site is steep. ISO 11074-1:1996 2.7 monitoring process of repetitive observation, for defined purposes, of one or more elements of the environment according to pre-arranged schedules in space and time using comparable methods for envir

40、onmental sensing and data collection 2.8 monitoring site area in which investigations will take place NOTE Areas which are relatively homogeneous are usually chosen. 2.9 point-source input input of a substance from a stationary discrete source of definite size NOTE 1 The sources can be stack emissio

41、ns, accidental spills, waste dumps, spills on industrial sites, major leaks from sewers and other pipelines. NOTE 2 Point-source input can cause both locally contaminated sites and relatively uniformly contaminated sites. ISO 11074-1:1996 2.10 risk assessment assessment of damaging effects of a poll

42、uted site on man and the environment with respect to their nature, extent and probability of occurrence ISO 11074-1:1996 2.11 sample portion of material selected from a large quantity of material ISO 11074-2:1998 2.12 sampling process of drawing or constituting a sample ISO 3534-1:1993 DIN EN ISO 16

43、133:2011-09 EN ISO 16133:2011 (E) 6 NOTE For the purpose of soil investigation, “sampling” also relates to selection of locations for the purpose of in situ testing carried out in the field without removal of material. ISO 11074-2:1998 2.13 sampling point location within the monitoring site at which

44、 physical sampling takes place 2.14 sampling procedure operational requirements and/or instructions relating to the use of a particular sampling plan ISO 11074-2:1998 2.15 soil damage alteration of soil properties which cause negative effects on one or more soil functions, human health or environmen

45、t ISO 11074-1:1996 2.16 substance input movement of a substance from another environmental compartment into a soil ISO 11074-1:1996 2.17 substance output movement of a substance from the soil into another environmental compartment ISO 11074-1:1996 2.18 uniformly contaminated site site with a general

46、ly uniform concentration of a substance hazardous to soil NOTE The extent of the contamination is usually large and the gradient of concentration within the site is rather shallow. ISO 11074-1:1996 3 Monitoring objectives 3.1 General Monitoring is an important tool for the early detection of environ

47、mental impact on soil and soil processes. It thus has a major role in the prevention or minimization of environmental damage or the detection of environmental improvement. By the early detection of environmental impact, or the potential for such impact, a monitoring programme could help to reduce or

48、 remove the costs of reaching or maintaining a given level of environmental management, protection or quality. Monitoring programmes can also be used to evaluate the outcome of environmental policies, to assist in the development of strategies for soil protection and environment management. They can

49、 also serve as research DIN EN ISO 16133:2011-09 EN ISO 16133:2011 (E) 7 platforms for the development and validation of field and analytical methods and of models of soil and related environmental processes. The range of purposes for which soil-monitoring programmes can be designed encompasses such a vast range of time scales, variables and processes that it is not possible to give specific guidance on the design of a monitoring programme to meet all the obj