EN 19694-6-2016 en Stationary source emissions - Determination of greenhouse gas (GHG) emissions in energy-intensive industries - Part 6 Ferroalloy industry《固定源排放 能源密集型工业中温室气体排放的测定.pdf

1、BS EN 19694-6:2016Stationary source emissions Determination of greenhousegas (GHG) emissions in energy-intensive industriesPart 6: Ferroalloy industryBSI Standards PublicationWB11885_BSI_StandardCovs_2013_AW.indd 1 15/05/2013 15:06BS EN 19694-6:2016 BRITISH STANDARDNational forewordThis British Stan

2、dard is the UK implementation of EN 19694-6:2016.The UK participation in its preparation was entrusted to TechnicalCommittee EH/2/1, Stationary source emission.A list of organizations represented on this committee can beobtained on request to its secretary.This publication does not purport to includ

3、e all the necessaryprovisions of a contract. Users are responsible for its correctapplication. The British Standards Institution 2016. Published by BSI StandardsLimited 2016ISBN 978 0 580 87117 7ICS 13.040.40Compliance with a British Standard cannot confer immunity fromlegal obligations.This British

4、 Standard was published under the authority of theStandards Policy and Strategy Committee on 31 July 2016.Amendments issued since publicationDate Text affectedBS EN 19694-6:2016EUROPEAN STANDARD NORME EUROPENNE EUROPISCHE NORM EN 19694-6 July 2016 ICS 13.040.40 English Version Stationary source emis

5、sions - Determination of greenhouse gas (GHG) emissions in energy-intensive industries - Part 6: Ferroalloy industry missions de sources fixes - Dtermination des missions de gaz effet de serre (GES) dans les industries nergo-intensives - Partie 6: Industrie des ferro-alliages Emissionen aus stationr

6、en Quellen - Bestimmung von Treibhausgasen (THG) aus energieintensiven Industrien - Teil 6: Ferrolegierungsindustrie This European Standard was approved by CEN on 5 May 2016. CEN members are bound to comply with the CEN/CENELEC Internal Regulations which stipulate the conditions for giving this Euro

7、pean 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 three official version

8、s (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 bodies of Austria, Be

9、lgium, 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, Spain, Sweden, Swit

10、zerland, Turkey andUnited Kingdom. EUROPEAN COMMITTEE FOR STANDARDIZATION COMIT EUROPEN DE NORMALISATION EUROPISCHES KOMITEE FR NORMUNG CEN-CENELEC Management Centre: Avenue Marnix 17, B-1000 Brussels 2016 CEN All rights of exploitation in any form and by any means reserved worldwide for CEN nationa

11、l Members. Ref. No. EN 19694-6:2016 EBS EN 19694-6:2016EN 19694-6:2016 (E) 2 Contents Page European foreword . 3 Introduction 4 1 Scope 6 2 Normative references 6 3 Terms and definitions . 6 4 Symbols and abbreviations . 8 5 Determination of GHGs Principles . 9 5.1 General 9 5.2 Major GHG in ferro-a

12、lloys. 9 5.3 Determination based on mass balance . 9 5.4 Use of waste gas/heat recovery . 9 6 Boundaries 9 6.1 General 9 6.2 Operational boundaries 9 6.3 Organizational boundaries . 10 7 Direct emissions and their determination 11 7.1 General . 11 7.2 Mass balance approach 11 7.3 Process emissions 1

13、5 7.4 Combustion emissions . 17 7.5 Combustion of biomass fuels . 19 8 Indirect emissions . 19 8.1 General . 19 8.2 CO2from external electricity production 19 9 Baselines, acquisitions and disinvestments . 20 10 Reporting 20 10.1 General . 20 10.2 Reporting periods 21 10.3 Performance indicators . 2

14、1 11 Uncertainty of GHG inventories 23 11.1 Introduction to uncertainty assessment . 23 11.2 Uncertainty of activity data 24 11.3 Uncertainties of fuel and material parameters . 24 11.4 Evaluation of the overall uncertainty of an GHG inventory 25 Annex A (normative) Tier 1 emission factors . 26 Anne

15、x B (normative) Minimum frequency of analysis 28 Annex C (normative) Country-wise emission factors for electricity 29 Bibliography . 33 BS EN 19694-6:2016EN 19694-6:2016 (E) 3 European foreword This document (EN 19694-6:2016) has been prepared by Technical Committee CEN/TC 264 “Air quality”, the sec

16、retariat 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 2017, and conflicting national standards shall be withdrawn at the latest by January 2017. Attention is dr

17、awn 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 has been prepared under a mandate M/478 given to CEN by the European Commission and the

18、 European Free Trade Association. EN 19694, Stationary source emissions Determination of greenhouse gas (GHG) emissions in energy-intensive industries is a series of standards that consists of the following parts: Part 1: General aspects Part 2: Iron and steel industry Part 3: Cement industry Part 4

19、: Aluminium industry Part 5: Lime industry Part 6: Ferroalloy industry 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, Cyprus, Czech Republic, Denmar

20、k, 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, Spain, Sweden, Switzerland, Turkey and the United Kingdom. BS EN 19694-6:20

21、16EN 19694-6:2016 (E) 4 Introduction Overview of the ferro-alloy manufacturing process Ferroalloy production involves a metallurgical reduction process that results in significant carbon dioxide emissions. These emissions are the results of a carbothermic reaction which is intrinsic to the process.

22、In ferroalloy production, ore, carbon materials and slag forming materials are mixed and heated to high temperatures for smelting. Submerged Electric Arc Furnaces (SEAF) with graphite electrodes, self- baking Sderberg or composite electrodes is the main process to produce ferro-alloys in Europe (see

23、 Figure 1). Smelting in an electric arc furnace is accomplished by conversion of electrical energy to heat. An alternating current applied to the electrodes creates current to flow through the charge between the electrode tips. The heat is produced by the electric arcs and by the resistance in the c

24、harge materials. Emissions from the smelting process are therefore not to combustion emissions. The furnaces may be open, semi-closed or closed. The reduction process is the main source of direct CO2emissions. Other CO2sources include direct emissions from calcination of calcium, magnesium and other

25、 carbonates (e.g. limestone) in some processes and from non-smelting fuels (e.g. dryers for ladles and refractory linings, room heating), and indirect emissions from, e.g. external power production. Figure 1 Submerged Electric Arc Furnace (SEAF) CO2from the smelting of raw materials CO2emissions fro

26、m reducing agents and electrode use In the smelting process, CO2is released due to the carbothermic reduction of the metallic oxides occurring with the consumption of both carbonaceous reductants and carbon based electrodes. The carbon in the reductants reacts with oxygen from the metal oxides to fo

27、rm CO and then CO2(in different BS EN 19694-6:2016EN 19694-6:2016 (E) 5 ways depending on the process), and the ores are reduced to molten base metals. For calculation, the assumption is that all CO is assumed to be converted in the furnace to CO2. The reductant carbon is used in the form of coke, c

28、oal, pet coke, anthracite, charcoal and wood-chips. The first four are fossil based and the charcoal and wood-chips are bio-carbon. In the carbothermic process, only the fixed carbon content is used as a reducing agent, which means that volatile matter, ashes and moisture mostly leave the furnace wi

29、th the off-gas and slag. The nature of reducing agents, price and electrodes is depending of the localization of the plant, the raw material availability and it is presented in Table 1. It is variable from one site to another and from one year to another and also from one ferro-alloy to another. Tab

30、le 1 Type of reducing agents and electrodes used in the electrometallurgy Sector Reducing agents Electrodes Crude petroleum coke Graphite electrode Calcinated petroleum coke Prebaked electrodes Coal coke Sdeberg paste Coke from coal Composite electrode Wood Calcinated wood Charcoal Graphite powder A

31、nthracite CO2emissions are estimated with/calculated from the consumption of the reducing agents and electrodes, their carbon content and the carbon content of the final products1. ores + reducing agent ferro-alloys/metal* + CO2+ dust/by-product (i.e. slags)* * amount of carbon can be found in the p

32、roducts Default emission factors suggested in these documents are used, except where more recent, industry-specific data has become available. 1The basic calculation methods used in this standard are compatible with the 2006 IPCC Guidelines for National Greenhouse Gas Inventories issued by the Inter

33、governmental Panel on Climate Change (IPCC), and with the Regulation 601/2012 but the objectives of this standards are of different nature implying that the data gathered can cover a broader (or reduced) boundaries as compared to the objectives of the Regulation. BS EN 19694-6:2016EN 19694-6:2016 (E

34、) 6 1 Scope This European Standard provides a harmonized methodology for calculating GHG emissions from the ferro-alloys industry based on the mass balance approach2. It also provides key performance indicators over time of ferro-alloys plants. It addresses the following direct and indirect sources

35、of GHG: Scope 1 Direct GHG emissions from sources that are owned or controlled by the company, such as emissions result from the following sources: smelting (reduction) process; decomposition of carbonates inside the furnace; auxiliaries operation related to the smelting operation (i.e. aggregates,

36、drying processes, heating of ladles, etc.). Scope 2 Indirect GHG emissions from: the generation of purchased electricity consumed in the companys owned or controlled equipment. This European Standard is to be used in conjunction with EN 19694-1, which contains generic, overall requirements, definiti

37、ons and rules applicable to the determination of GHG emissions for all energy-intensive sectors, provides common methodological issues and defines the details for applying the rules. The application of this standard to the sector-specific standards ensures accuracy, precision and reproducibility of

38、the results and is for this reason a normative reference standard. The requirements of these standards do not supersede legislative requirements. 2 Normative references The following documents, in whole or in part, are normatively referenced in this document and are indispensable for its application

39、. For dated references, only the edition cited applies. For undated references, the latest edition of the referenced document (including any amendments) applies. EN 19694-1:2016, Stationary source emissions Determination of greenhouse gas (GHG) emissions in energy intensive industries Part 1: Genera

40、l aspects 3 Terms and definitions For the purposes of this document, the terms and definitions in EN 19694-1 and the following apply. 3.1 auxiliaries equipment consuming electricity/power related to the smelting process: fans, pumps, gas abatement systems (filter bags, venture scrubbers, etc.) 3.2 s

41、ilica fume amorphous silicon dioxide particles from the volatilization and vaporization of furnace feed materials in the manufacture of ferrosilicon and silicon, the process off-gas that contains silica fumes beings cleaned in a baghouse using fabric filters of the open or semi-closed SEAF 2Based on

42、 European Commission Regulation 601/2012. BS EN 19694-6:2016EN 19694-6:2016 (E) 7 3.3 ferro-alloy term used to describe concentrated alloys of iron and one or more metals such as silicon, manganese, chromium, molybdenum, vanadium or tungsten 3.4 silicon metalloid produced by carbo-thermic reduction

43、of quartz in an electric submerged arc furnace 3.5 smelting industrial process where one or more ores or ore concentrates are heated and reduced (i.e. chemically modified) by, e.g. aluminino-carbo-silico thermic reduction to manufacture and mix the metals in one step EXAMPLE Examples of smelted allo

44、ys are ferro-alloys. 3.6 Submerged Electric Arc Furnace SEAF electric arc-heating furnace in which the arcs are completely submerged under the charge. The arc forms between the electrode (graphite electrodes or self- baking Sderberg electrodes) and metal surface or bottom lining. The heat being prod

45、uced by the electric arcs and by the resistance in the charge materials initiates the reduction process. The furnaces may be open, semi-closed or closed, which can depend upon the ferro-alloy to be produced. A commonly used technology is the submerged-arc (electric) furnace (SEAF). 3.7 fossil fuels

46、all fossil fuels listed by IPCC or any fuel which contains organic and inorganic carbon that is not biomass 3.8 biomass fuels fuels with only biogenic carbon 3.9 Petcoke petroleum coke, a carbon-based solid fuel derived from oil refineries 3.10 sintering/sinter process to form a coherent mass by hea

47、ting without melting 3.11 Sderberg electrodes continuously self-baking carbon electrode used in electro-metallurgical furnaces for production of ferroalloys and silicon (the “Sderberg paste” is a preparation of coal tar pitch and carbonaceous dry aggregate) 3.12 composite electrodes in composite ele

48、ctrodes the core is composed of graphite while the exterior is a self-baking carbon paste (which is a “Sderberg paste”) BS EN 19694-6:2016EN 19694-6:2016 (E) 8 3.13 pre-baked electrodes carbonaceous paste (a mixing of coal tar pitch with a dry carbonaceous aggregate) is baked so as to carbonize coal

49、 tar pitch in order to form a solid pitch coke binder phase 4 Symbols and abbreviations For the purposes of this document, the following symbols and abbreviations apply. AF alternative fuels CO carbon monoxide CO2carbon dioxide EF emission factor EU ETS The CO2Emissions Trading Scheme of the European Union FA ferro-alloys FABP ferro-alloys and related by-products GHG greenhouse gases GJ giga joule IPCC Intergovernmental Panel on Climate Change KPI key performance indicator LHV lower heat value (synonym for net calorifi