CEN TR 15591-2007 Solid recovered fuels - Determination of the biomass content based on the 14C method《固体再生材料 塑料制品 基于C-14法测定生物的数量》.pdf

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1、PUBLISHED DOCUMENTPD CEN/TR 15591:2007Solid recovered fuels Determination of the biomass content based on the 14C methodICS 75.160.10g49g50g3g38g50g51g60g44g49g42g3g58g44g55g43g50g56g55g3g37g54g44g3g51g40g53g48g44g54g54g44g50g49g3g40g59g38g40g51g55g3g36g54g3g51g40g53g48g44g55g55g40g39g3g37g60g3g38g5

2、0g51g60g53g44g42g43g55g3g47g36g58PD CEN/TR 15591:2007This Published Document was published under the authority of the Standards Policy and Strategy Committee on 30 April 2007 BSI 2007ISBN 978 0 580 50522 5National forewordThis Published Document was published by BSI. It is the UK implementation of C

3、EN/TR 15591:2007.The UK participation in its preparation was entrusted to Technical Committee PTI/17, Solid biofuels.A list of organizations represented on PTI/17 can be obtained on request to its secretary.This publication does not purport to include all the necessary provisions of a contract. User

4、s are responsible for its correct application.Amendments issued since publicationAmd. No. Date CommentsTECHNICAL REPORT RAPPORT TECHNIQUE TECHNISCHER BERICHT CEN/TR 15591 February 2007 ICS 75.160.10 English Version Solid recovered fuels - Determination of the biomass content based on the 14C method

5、Combustibles solides de rcupration - Dtermination de la teneur en biomasse, base sur la mthode du C14Feste Sekundrbrennstoffe - Bestimmung des Gehaltes an Biomasse nach de 14C-Methode This Technical Report was approved by CEN on 1 January 2007. It has been drawn up by the Technical Committee CEN/TC

6、343. 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, Sp

7、ain, 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 CEN All rights of exploitation in any form and by any means reserved worldwide for CEN nationa

8、l Members. Ref. No. CEN/TR 15591:2007: E2 Contents Page Foreword3 0 Introduction4 1 Scope 7 2 Terms and definitions .7 3 Symbols and abbreviations 7 4 Methods of measurement .8 4.1 Principle8 4.2 Sampling.8 4.3 Transport and storage.8 4.4 Preparation of the test portion from the laboratory sample .9

9、 4.5 Analysis by Proportional Scintillation-counter Method (PSM) .9 4.6 Analysis by -ionisation (proportional gas counting) (BI)10 4.7 Analysis by Accelerator Mass Spectrometry (AMS) 10 5 Equipment and reagents.10 5.1 For the preparation of the test portion 10 5.2 For the analysis by PSM .11 5.3 For

10、 the analysis by -ionisation (BI) .11 5.4 For analysis by AMS (example from Utrecht University).11 6 Procedure .11 6.1 For sampling 11 6.2 For the preparation of the test portion 12 6.3 Procedure for analysis 13 7 Calculations13 7.1 General13 7.2 Calibration 14 7.3 Example for the calculation of a R

11、DF sample analysed with PSM .15 8 Uncertainty of measurement (PMS and BI measurements) based in Poisson statistics.15 9 Strengths and weaknesses.16 9.1 Comparison of 14C based methods with SDM 16 9.2 Comparison of PSM, Gas Counting (BI) and AMS .17 10 Legislative aspects17 10.1 General17 10.2 Austri

12、a.17 10.3 The Netherlands.17 10.4 Finland 18 11 Conclusions .18 Annex A (informative) Origin of expertise present in the technical report19 Annex B (informative) List of European labs with radio carbon expertise.22 Bibliography 33 CEN/TR 15591:20073 Foreword This document (CEN/TR 15591:2007) has bee

13、n prepared by Technical Committee CEN/TC 343 “Solid recovered fuels”, the secretariat of which is held by SFS. Attention 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

14、 all such patent rights. CEN/TR 15591:20074 0 Introduction 0.1 General This document has been prepared as a result of the CEN/TC 343/WG 3 meeting in Amsterdam in April 2005. It summarizes the state of the art in 14C-based methods applied to determining the biomass content of SRF; as of yet no techni

15、cal CEN standards for the application of 14C-based methods to determine biomass content are available. The purpose of this Technical Report is to present the information available on this subject at this moment to assess if an extension of the available methods for determining the biomass content of

16、 SRF is required, wanted and technically possible. Analytically proven standards exist for determining the biomass content of SRF by manual sorting and by selective dissolution (CEN/TS 15440 1). In the Netherlands these methods are available as NTA (National Technical Agreement) and have been in use

17、 for some years. Important advantages of these standards are their applicability using basic laboratory equipment and available personnel. However, they are not applicable to all kinds of solid recovered fuels. The manual sorting method fails if the constituents of the sample are shredded too finely

18、, if they are strongly intertwined or compressed or if they cannot be recognized visually. The selective dissolution method fails if biomass constituents are present that do not dissolve, or fossil components that do. Both methods fall short if fossil and biomass carbon are mixed at the molecular le

19、vel. 14C based methods do not use chemical or morphological properties of the sample but physical properties of the carbon atoms themselves. Because 14C based methods are based on these physical properties they avoid the problems of manual sorting and selective dissolution methods. On the other hand

20、 they need more instrumentation and skilled personnel. They are proposed here as an addition to the manual sorting and selective dissolution methods because they resolve analytical problems that are otherwise irresolvable. The application of 14C based methods for similar purposes are not new 2 3. In

21、 this document the information available in Europe and the USA concerning biomass carbon content determination in solid recovered fuels with 14C based methods is presented to give the reader background information about possibilities and drawbacks of these methods. 0.2 Basis of the 14C method The 14

22、C method is a well-known method in global use, for determining the age of carbon containing matter. 14C is a radioactive isotope; its presence in the air is a result of the interaction of cosmic radiation and the nitrogen in the atmosphere (see Figure 1). Fossil carbon contains no 14C, however a tra

23、ce amount of 14C is present in living matter. The 14C isotope is quickly converted to 14CO2after formation and enters living matter when atmospheric 14CO2is converted in the biosphere by photosynthesis to sugars and further converted to e.g. cellulose. The concentration of 14C in air is considered c

24、onstant all over the world. In living material the concentration of 14C is stable and in equilibrium with the air concentration. In dead material the concentration of 14C slowly diminishes to zero as the radioactive 14C isotope decays. Measuring the amount of 14C in solid recovered fuels is the basi

25、s for determining biomass content based on the 14C method. CEN/TR 15591:20075 Figure 1 Illustration of the basis of the 14C method Organic material is used for many purposes. One of the objectives is direct use as a fuel which is outside the scope of this report. However, after completing their prim

26、ary use, many of these organic materials may ultimately be used in the form of solid recovered fuels. Examples of organic materials in solid recovered fuels are: Packaging materials; Paper; Wood used in buildings; Kitchen waste; Waste (dung and offal) from the bio industry; Plastics; Car tires. Carb

27、on present in material produced by living organisms, immobilized as fuel in present times is called biomass. Carbon present in material produced by living organisms immobilized as fuel in a past geological era is called fossil fuel. The difference between the two is that CO2from biomass or biomass o

28、rigin does not CEN/TR 15591:20076 contribute to a higher concentration of CO2in the atmosphere as its carbon has been recently extracted from the atmosphere. In solid recovered fuels, the combustible carbon originates from fossil (mainly in the form of plastics), mixed sources like rubber tyres and

29、packaging materials, and from biomass origin (e.g. wood, paper). Authorities require that emissions of CO2from fossil origin by companies is made known, thus, in order to determine these companies, knowledge about the biomass content by total carbon content of mixed fuels should be acquired. For thi

30、s reason, methods such as the solid dissolution method and 14C method were developed. International acceptance of a 14C based method can be expected, as can be illustrated by the recent publication of ASTM, ASTM D 6866-05, Standard Test Method for determining the Bio based Content of Natural Range M

31、aterials Using Radiocarbon and Isotope Ratio Mass Spectrometry Analysis2. CEN/TR 15591:20077 1 Scope This Technical Report gives an overview of the suitability of 14C-based methods for the determination of the fraction of biomass carbon in solid recovered fuels, using detection by scintillation, gas

32、 ionization and mass spectrometry. 2 Terms and definitions For the purposes of this document, the following terms and definitions apply. 2.1 biodegradable carbon mass fraction of the total carbon that is capable of undergoing biological anaerobic or aerobic decomposition under conditions naturally o

33、ccurring in the biosphere 2.2 biogenic carbon mass fraction of total carbon that was produced in natural processes by living organisms but not fossilized or derived from fossil resources 2.3 biomass carbon equivalent to biogenic carbon 2.4 isotope abundance fraction of atoms of a particular isotope

34、of an element 2.5 repeatability extent of the agreement between the results of subsequent measurements of the same quantity, performed under the same measuring conditions 2.6 reproducibility extent of the agreement between the results of measurements of the same quantity, performed under variable me

35、asuring conditions. 3 Symbols and abbreviations This Technical Report uses the following symbols and abbreviations: 14C Carbon isotope with an atomic mass of 14 AMS Accelerator Mass Spectrometry Beta particle, electron emitted during radioactive decay BI eta Ionisation CEN/TR 15591:20078 BP Before P

36、resent (before 1950) CPM Counts per minute DPM Disintegrations per minute ETS Emissions Trading Scheme GM Geiger Mller LSC Liquid Scintillation Counter or Liquid Scintillation Counting PSM Proportional Scintillation-counter Method PMT Photo Multiplicator Tube RSD Relative Standard Deviation SDM Sele

37、ctive Dissolution Method SRF Solid Recovered Fuel STP Standard Temperature and Pressure (273,15 K (or 0 C) and 101,325 Pa (or 760 mmHg) 4 Methods of measurement 4.1 Principle The principle of the 14C method is to determine the biomass content by total carbon by measuring the amount of 14C present in

38、 the sample. This method utilizes the isotope abundance of 14C similar to the way the age of objects is measured for archaeological purposes. In all organisms living ashore, 14C has a known isotope abundance equal to its isotope abundance in atmospheric CO2. As soon as an organism dies, the isotope

39、abundance of 14C in its organic material starts to decrease because 14Cis an unstable isotope with a half-life of 5 730 yr. The isotope abundance of 14C may be considered zero after ten half lives or 60 000 yr. The biomass content by total carbon of a material is calculated as the proportion of the

40、isotope abundance of 14C in that material and the isotope abundance of 14C in the atmosphere at the time when the biomass was laid down. The method is especially useful for determining biomass carbon content, however, the relationship between biomass carbon content and biomass content should be dete

41、rmined for every type of waste; a limitation that is also valid for other existing methods. When information is available about how carbon atoms are chemically bound, the amount of bio energy can be calculated. 4.2 Sampling For the 14C based methods sampling procedures that are similar to those for

42、determining major elements 4 are used. As carbon is one of the major components in solid recovered fuel, problems with homogeneity are not to be expected with laboratory samples. Typical particle size of the sample material should be 0,2 mm. 4.3 Transport and storage For transport and storage of the

43、 samples, the same requirements are fulfilled as for normal lab samples. As part of the solid recovered fuel consists of organic material, dry and cool storage is applied to prevent conversion of the biomass part by microbiological activities. CEN/TR 15591:20079 4.4 Preparation of the test portion f

44、rom the laboratory sample For the PSM and BI methods sample sizes of 1 g or more are used. However at the 1 g level problems still arise with homogeneity of the sample; the use of a lab scale combustion device (e.g. rotary kiln) is recommended, allowing sample amounts of 5 g to 20 g. The AMS method

45、only needs a few milligrams of sample. In this case combustion of samples at a scale of approximately 1g is necessary. After combustion the carbon is present in a gas phase as CO2, and the next step is preparing a mg size sample from the gaseous combustion products. 4.5 Analysis by Proportional Scin

46、tillation-counter Method (PSM) PSM (also called Liquid Scintillation Counter method, LSC) determines the isotope abundance of 14C indirectly through its emission of (beta, electron) particles. The particles are detected through interacting with a solution of a scintillation molecule. This is possibl

47、e only if the carbon is homogeneously distributed in the solution, as the particles must be able to interact with the solution instead of being quenched in the solid fuel. Homogeneous distribution may be attained by four different methods: Conversion to CO2, followed by absorption in an organic amin

48、e and mixing this absorbent with the scintillation fluid. The amine is produced using fossil carbon, in order not to cause a blank signal. Conversion to CO2, followed by absorption in a BaCl2or CaCl2solution, and after drying and grinding, transfer of BaCO3or CaCO3into the scintillation fluid formin

49、g a suspension; or regeneration of CO2from the precipitate, which is absorbed in an organic amine, and mixing this absorbent with the scintillation fluid. Conversion to CO2, followed by adsorption on a solid medium, regeneration of CO2which is absorbed in an organic amine, and mixing this absorbent with the scintillation fluid. Liquid fuels may be directly mixed with the scintillation fluid. The scintillation fluid consists of a solvent and a dissolved fluorescent agent, the fluor. When a is emitted, it rapidly transfer