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International Aluminium Institute | www.world-aluminium.org International Aluminium Institute Results of the 2012 Anode Effect Survey Report on the Aluminium Industry’s Global Perfluorocarbon Gases Emissions Reduction Programme

2012 Anode Effect Survey Report - World Aluminium · 2013. 8. 20. · Anode Effect Overvoltage (AEO), the average cell voltage (in millivolts) above the target operating voltage,

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  • International Aluminium Institute | www.world-aluminium.org

    International Aluminium Institute

    Results of the 2012 Anode Effect Survey Report on the Aluminium Industry’s Global Perfluorocarbon Gases Emissions Reduction Programme

  • International Aluminium Institute | www.world-aluminium.org

    Contents Summary & Conclusions .......................................................................................................... 1

    Industry Trends ........................................................................................................................ 2

    2012 Anode Effect Survey ........................................................................................................ 3

    Global Emissions Estimations .................................................................................................. 9

    Uncertainties .......................................................................................................................... 12

    Benchmark Data ..................................................................................................................... 13

    Appendix A – Facility Emissions Calculation Methodologies ................................................. 19

    Tables Table 1 – Aluminium smelting technology categories .............................................................. 3

    Table 2 - 2012 Anode Effect Survey participation by technology, with respect to global aluminium production ............................................................................................................... 4

    Table 3 – Perfluorocarbon emission results from facility data reporting to the 2012 Anode Effect Survey ............................................................................................................................ 7

    Table 4 – Production weighted mean PFC emissions per unit production of reporting entities, 2006-2012 ................................................................................................................................ 8

    Table 5 – Total global 2012 PFC emissions ........................................................................... 10

    Table 6 - Slope and overvoltage coefficients by technology, including uncertainty (Source: IPCC, 2006) ............................................................................................................................ 19

  • International Aluminium Institute | www.world-aluminium.org

    Figures Figure 1 –Location of primary aluminium production, 1990 & 2006-2012 (SOURCE: IAI & CRU) ........................................................................................................................................ 2

    Figure 2 – Primary aluminium smelting technology mix, 1990-2011 (SOURCE: IAI & CRU) .. 2

    Figure 3 – 2012 Anode Effect Survey reporter aluminium production coverage by technology ................................................................................................................................................. 4

    Figure 4 – 2012 Anode Effect Survey reporter PFC emissions (as CO2e) coverage by technology ................................................................................................................................ 4

    Figure 5 – Reporting production & rate 1990-2012 .................................................................. 5

    Figure 6 – Median PFC emission rates (as CO2e) per tonne of production of reporting entities, per technology, 2006-2012 ......................................................................................... 8

    Figure 7 – Reporting rates (aluminium production) per technology, 2006-2012 ...................... 8

    Figure 8 – PFC emissions (as CO2e) per tonne of aluminium production, 2006-2012 .......... 10

    Figure 9 – Absolute PFC emissions (as CO2e) and primary aluminium production, 1990-2012 ....................................................................................................................................... 11

    Figure 10 – PFC emissions (as CO2e per tonne Al) performance of reporters, benchmarked as cumulative fraction within technologies, 2012 ................................................................... 14

    Figure 11 –PFC emissions performance of reporters (t CO2e/t Al), benchmarked as cumulative production within technologies, 2012 ................................................................... 14

    Figure 12 - PFC emissions performance of reporters (t CO2e/t Al), benchmarked as cumulative production within technologies, 1990 & 2012 ....................................................... 15

    Figure 13 - Average anode effect frequency of reporters benchmarked by technology type, 2012 ....................................................................................................................................... 16

    Figure 14 - Average anode effect duration of reporters benchmarked by technology type, 2012 ....................................................................................................................................... 16

    Figure 15 - Average anode effect minutes per cell day of reporters benchmarked by technology type, 2012 ............................................................................................................ 17

    Figure 16 - Average anode effect overvoltage of reporters benchmarked by technology type, 2012 ....................................................................................................................................... 18

  • 1

    International Aluminium Institute | www.world-aluminium.org

    Summary & Conclusions Global aluminium industry 2012 PFC emissions (as CO2e) per tonne of production (calculated to be 0.56 t CO2e/t Al) were 30% lower than those in 2006. With PFC emissions per tonne cut by almost 90% since 1990 and strong growth in aluminium production over the same period, total annual emissions of PFCs to the atmosphere by the aluminium industry have been reduced by 71% while primary aluminium production has increased by 135%.

    Survey data is published on the International Aluminium Industry (IAI)’s website. The IAI online statistical system does not report separate company data, but rather aggregates PFC emissions by different technologies. http://www.world-aluminium.org/statistics/perflurocarbon-pfc-emissions/#data

    The IAI PFC Emissions Reduction Voluntary Objective (2006-2020)

    The primary aluminium industry seeks to achieve the long term elimination of perfluorocarbon (PFC) emissions.

    Following an 86% reduction in PFC emissions per tonne of primary aluminium produced between 1990 and 2006, the global aluminium industry will further reduce emissions of PFCs per tonne of aluminium by at least 50% by 2020 as compared to 2006.

    The IAI is striving to increase the global aluminium production coverage of its annual Surveys to over 80%.

    Based on IAI annual survey results, by 2020 IAI member companies commit to operate with PFC emissions per tonne of production no higher than the 2006 global median level for their technology type.

    Progress will be monitored and reported annually and reviewed periodically by a recognised and independent third party. There will be interim reviews to ensure progress towards achievement of the 2020 objective.

  • 2

    International Aluminium Institute | www.world-aluminium.org

    Industry Trends Growth in primary aluminium production continues to be driven by China and the Arabian Gulf. Global primary aluminium production in 2012 was a record 46 million tonnes.

    Figure 1 –Location of primary aluminium production, 1990 & 2006-2012 (SOURCE: IAI & CRU)

    Figure 2 – Primary aluminium smelting technology mix, 1990-2012 (SOURCE: IAI & CRU)

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    NB:technology category details in Table 1

  • 3

    International Aluminium Institute | www.world-aluminium.org

    2012 Anode Effect Survey

    Survey Process The International Aluminium Institute has collected anode effect data directly from primary aluminium producers for the purposes of calculating sectoral PFC emission inventories for over a decade, with annual surveys carried out since 2000.

    The IAI Anode Effect Survey requests data from all aluminium smelting facilities around the world, via IAI member companies (http://www.world-aluminium.org/about/members/), direct correspondence with non-member producers and regional industry associations. Facilities are requested, where possible, to report by potline, and to separate data from different technologies within a single plant. As well as anode effect process data, reporters are also asked for information that allows for quality control (by comparison against other facilities and within reporters’ data over time) and for the IAI to take a snapshot and monitor over time the adoption of anode effect mitigation technologies such as prediction and automatic termination software. The reporting form and guidelines (PFC001) can be found from the IAI website (http://www.world-aluminium.org/media/filer_public/2013/01/15/pfc001.pdf).

    BROAD TECHNOLOGY CATEGORY

    TECHNOLOGY CATEGORY

    ALUMINA FEED CONFIGURATION

    ACRONYM

    Prebake

    (anodes pre-baked)

    Centre Worked

    Bar broken centre feed CWPB Point centre feed PFPB

    Side Worked Manual side feed SWPB

    Søderberg (anodes baked in-situ)

    Vertical Stud

    Manual side feed Point feed

    VSS

    Horizontal Stud Manual side feed HSS Table 1 – Aluminium smelting technology categories

    Participation Rate It is significant that the 2012 survey results include data from 100% of SWPB, 100% of VSS and 99% of HSS technology production. On average, these technologies produce more emissions per tonne of aluminium produced than the CWPB and PFPB categories (see Table 3).

    As the aluminium production in China represents an increasing proportion of the industry, non-reported data are predominantly from China, the overall reporting rate shown in Figure 5 keeps decreasing. Outside of China, 20 smelters, representing around 4.6 million tonnes of production (equivalent to 10% of worldwide production), did not report 2012 anode effect data to IAI, compared to 91 smelters that did.

  • 4

    International Aluminium Institute | www.world-aluminium.org

    TECHNOLOGY

    2012 primary aluminium production

    (1,000 tonnes)

    2012 production represented in

    survey (1,000 tonnes)

    2012 participation rate by production

    CWPB 1,220 610 50%

    PFPB (Rest of World)

    19,680 15,666 80 % 39%

    PFPB (China) 20,267 0 0 %

    SWPB 606 606 100 %

    VSS 3,586 3,586 100 %

    HSS 543 540 99 %

    All Technologies (excluding China)

    25,562 21,006 82 %

    All Technologies (Including China)

    45,902 21,006 46 %

    Table 2 - 2012 Anode Effect Survey participation by technology, with respect to global aluminium production

    Note: any inconsistencies due to rounding

    The high coverage of the survey data outside China (with respect to both metal production and emissions) and of the higher emitting technologies, combined with the fact that actual measurements and secondary information are available to make an informed estimate of Chinese industry performance, means that the IAI is able to develop estimates of PFC emissions from the global aluminium industry, with some degree of accuracy.

    Figure 3 – 2012 Anode Effect Survey reporter aluminium production coverage by technology

    Figure 4 – 2012 Anode Effect Survey reporter

    PFC emissions (as CO2e) coverage by technology

    Reporting PFPB & CWPB

    Reporting SWPB

    Reporting Søderberg

    Non Reporting PFPB (China)

    Non Reporting PFPB & CWPB (ROW)

    Non Reporting Søderberg

  • 5

    International Aluminium Institute | www.world-aluminium.org

    Figure 5 – Reporting production & rate 1990-2012

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  • 6

    International Aluminium Institute | www.world-aluminium.org

    Data Requested Annual (1 January – 31 December 2012) data required include:

    Annual primary aluminium metal production (MP), the mass of molten metal (in metric tonnes) tapped from pots in reporting period;

    Anode effect frequency (AEF), the average number of anode effects occurring per cell day over the reporting period;

    Anode effect duration (AED), the average time (in minutes) of each anode effect over the reporting period;

    Anode Effect Overvoltage (AEO), the average cell voltage (in millivolts) above the target operating voltage, when on anode effect, over the reporting period.

    Overvoltage is specifically requested from operators employing Rio Tinto Alcan AP-18 or AP-3x PFPB technologies and SWPB facilities using control technology that records overvoltage rather than anode effect duration. These anode effect performance data allow for the calculation, by the Intergovernmental Panel on Climate Change (IPCC) Tier 2 or Tier 3 methodologyF1F, of facilities’ total annual tetrafluoromethane (CF4) and hexafluoroethane (C2F6) emissions, and hence tonnes of CO2 equivalent (CO2e) emitted per tonne of aluminium produced.

    It should be noted that the IPCC Tier 1 methodology of multiplying metal production by a technology-specific coefficient to estimate PFC emissions is not good practice, as the results are not derived from process data and consequently have a very high uncertainty attached to them. IAI does not use the Tier 1 methodology in any of its PFC emissions calculations.

    2012 Survey Results Anode effect data was collected from 230 reporting entities (smelters & potlines) representing 21 million tonnes of primary aluminium production Results are summarised in Table 3 below.

    Facilities that have made PFC measurements by which Tier 3 calculation of PFC emissions is possible account for 58% of the total reported CF4 emissions from survey participants. It should be noted that Tier 3 calculations typically carry an uncertainty of +/- 15%, with well controlled systems down to +/- 12%, while uncertainty in Tier 2 calculations can be as high as +/- 50%."

    1 2006 IPCC Guidelines for National Greenhouse Gas Inventories, Primary Aluminium Production, Chapter 3,Section 4.4, http://www.ipcc-nggip.iges.or.jp/public/2006gl/pdf/3_Volume3/V3_4_Ch4_Metal_Industry.pdf.

  • 7

    International Aluminium Institute | www.world-aluminium.org

    Technology IPCC Tier Number of reporting entities

    Reported production

    (kt Al)

    Total CF4 emissions(Gg CF4)

    Total C2F6 emissions(Gg C2F6)

    Median CF4 emission

    factor (kg CF4/t Al)

    Median C2F6 emission

    factor (kg C2F6/t

    Al)

    Mean C2F6: CF4 weight

    ratio

    Total PFC emissions2 (kt CO2e)

    Median PFC

    emission factor

    (t CO2e/t

    Mean PFC emission

    factor (t CO2e/t Al)

    CWPB 2 1 325 0.005 0.001

    0.025 0.004 0.15 116 0.20 0.19 3 1 285 0.010 0.002

    PFPB

    2 Slope 68 5,550 0.222 0.027

    0.026 0.003 0.11 3,954 0.19 0.25 3 Slope 32 5,790 0.150 0.015

    2 OV 18 2,565 0.095 0.011

    3 OV 8 1,761 0.062 0.004

    SWPB 2 5 154 0.089 0.022

    0.352 0.111 0.24 2,301 3.29 3.80 3 3 451 0.176 0.041

    VSS 2 22 915 0.161 0.009

    0.116 0.007 0.06 3,582 0.81 1.00 3 54 2,671 0.347 0.023

    HSS 2 14 290 0.033 0.003

    0.136 0.012 0.10 972 0.99 1.82 3 4 250 0.096 0.011

    ALL - 230 21,006 1.446 0.166 - - 0.12 10,926 - 0.52 Table 3 – Perfluorocarbon emission results from facility data reporting to the 2012 Anode Effect Survey

    Note: any inconsistencies due to rounding

    2 Carbon dioxide equivalent (CO2e) emissions for survey participants are calculated by multiplying the total tonnes of each PFC component gas by the Global Warming Potential (GWP) values reported in the IPCC Second Assessment Report (i.e. 6,500 for CF4 and 9,200 for C2F6). IPCC Second Assessment Report GWP values are employed to maintain consistency with Kyoto Protocol conventions and Clean Development Mechanism (CDM) and Joint Implementation (JI) accounting.

  • 8

    International Aluminium Institute | www.world-aluminium.org

    The range of anode effect and PFC emissions performance within technologies is explored further in the “Benchmark Data” section below. Changes in median emission performance (in t CO2e/t Al) within technologies between 2006 and 2012 are shown in the following chart. As can be seen, the higher emitting technologies have the highest reporting rates.

    Figure 6 – Median PFC emission rates (as CO2e) per tonne of production of reporting

    entities, per technology, 2006-2012

    Figure 7 – Reporting rates (aluminium production) per technology, 2006-2012

    Reported average (production weighted mean) PFC emissions (as CO2e) per tonne of production have been reduced by 36% between 2006 and 2012 (CF4 by 41%, C2F6 by 43%):

    Reporting

    production (kt Al)

    Reporting rate by production

    CF4 emission

    factor (kg CF4/t Al)

    C2F6 emission

    factor (kg C2F6/t Al)

    Total PFC emission

    factor (t CO2e/t Al)

    2012 21,006 46% 0.069 0.008 0.52

    2011 22,413 51 % 0.079 0.009 0.60

    2010 21,774 53 % 0.071 0.009 0.54

    2009 22,184 60 % 0.069 0.008 0.52

    2008 24,741 63 % 0.089 0.010 0.67

    2007 23,903 63 % 0.106 0.013 0.81

    2006 23,177 68 % 0.116 0.014 0.87 Table 4 – Production weighted mean PFC emissions per unit production of reporting entities, 2006-2012

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  • 9

    International Aluminium Institute | www.world-aluminium.org

    Global Emissions Estimations

    Methodology A more realistic picture of the global aluminium industry’s PFC emissions inventory should include some estimate of the non-reporting industry year on year. In fact, the IAI voluntary objective is an objective for the industry as a whole, not just IAI membership or reporting companies and so is based on such a global estimate.

    The IAI uses median PFC emissions performance per technology (as shown in Table 3 above) applied to non-reporting production by technology in order to calculate the global PFC emissions inventory from aluminium production.

    Non-reporting aluminium production tonnage data is taken from three sources. The majority (China 2012 primary aluminium production of 20,267,471 metric tonnes) is reported by the China Nonferrous Metals Industry Association (CNIA). Around 4 million tonnes of production (n=13) is from other IAI surveys – primarily IAI Form 100 “Primary Aluminium Production” (http://www.world-aluminium.org/media/filer_public/2013/01/15/iai_form_100.pdf). Finally, just under 770,000 metric tonnes of production is data kindly provided by the CRU Group (www.crugroup.com), for facilities where there is no direct IAI data collection (n=7).

    Accounting for China Recent (2008-2010) PFC emissions measurements at 13 PFPB facilities in China, undertaken as part of the Asia Pacific Partnership for Clean Development & Climate (www.asiapacificpartnership.org) and by the Aluminum Corporation of China (Chinalco), have yielded a median emission factor of 0.69 tonnes CO2e per tonne of aluminium produced (CF4 median 0.100 kg/t Al; C2F6:CF4 weight fraction 0.043); , compared with a PFPB survey reporter median performance of 0.19 tonnes CO2e per tonne of aluminium (0.026 kg CF4/t Al; C2F6:CF4 weight ratio = 0.11).

    This China-specific value (0.69 t CO2e/t Al) is applied to the 2012 Chinese non-reporting PFPB cohort, in place of the IAI PFPB survey median, and has also been applied to Chinese non-reporting production from 2006 to 2011, to derive a time series that more accurately reflects Chinese smelter performance and global emissions than one based on rest-of-world averages, albeit one that remains static over time.

    2012 Global Aluminium Industry PFC Emissions Summing the emissions and production data from reporting and non-reporting facilities and then dividing total global PFC emissions (t CO2e) by total global production (t Al), gives a production weighted average 2012 PFC emissions performance for the global aluminium industry of 0.56 tonnes of CO2e per tonne of primary aluminium produced, as outlined in Table 5 – Total global 2012 PFC emissions

  • 10

    International Aluminium Institute | www.world-aluminium.org

    Total PFC emissions

    (1,000 t CO2e)

    Total aluminium production

    (1,000 tonnes)

    PFC emission

    factor (t CO2e/t Al)

    Reported 10,926 21,006 0.52

    Calculated from non-reporters 14,864 24,895 0.60

    TOTAL GLOBAL 25,790 45,902 0.56 Table 5 – Total global 2012 PFC emissions

    Note: any inconsistencies due to rounding

    Global Aluminium Industry PFC Emissions Reduction Performance (1990-2012) Global PFC emissions (as CO2e) per tonne of production have been reduced by 31% since 2006, on course to meet the IAI voluntary objective of a 50% reduction by 2020 on a 2006 baseline. The 31% improvement since 2006 takes the overall improvement since 1990 to 87%.

    Figure 8 – PFC emissions (as CO2e) per tonne of aluminium production, 2006-2012

    With PFC emissions per tonne cut by almost 90% since 1990 and primary aluminium production having grown by 135% over the same period, absolute emissions of PFCs by the aluminium industry have been reduced from approximate 90 million tonnes of CO2e in 1990 to 26 million tonnes in 2012, a fall of over 70%.

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    International Aluminium Institute | www.world-aluminium.org

    Figure 9 – Absolute PFC emissions (as CO2e) and primary aluminium production, 1990-2012

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  • 12

    International Aluminium Institute | www.world-aluminium.org

    Uncertainties Understanding sources and magnitude of uncertainty in the calculation of global industry PFC emissions is important, not only in terms of the current emissions inventory and its relationship to top-down measurements of PFCs in the atmosphere, but also with respect to quantifying the industry’s performance over time.

    Given that the 2012 data presented above indicates a significant reduction in total PFC emissions (as CO2e) since 1990, it is necessary to consider the uncertainties inherent in the 1990 baseline number and the 2012 performance number and to quantify the probability that the reduction has been made.

    Potential significant sources of uncertainty include:

    the application of average industry IPCC Tier 2 calculation factors,

    use of Tier 2 factors for calculating PFC emissions for survey participants where suitable facility specific measurements are not available, and,

    estimates of PFC emissions for producers that do not participate in the anode effect survey.

    Uncertainty arises from the use of IPCC Tier 2 average industry factors due to the uncertainty in the mean slope and overvoltage coefficients. Additional PFC measurements will reduce the uncertainty of the mean coefficient values. However, for all technology groups there is considerable variance in the individual values of slope and overvoltage coefficients, from which the means are calculated. For this reason, calculations of PFC emissions with Tier 2 coefficients will be more uncertain than calculations made with Tier 3 coefficients, calculated from PFC measurements made using good measurement practices. Calculations of PFC emissions for non-reporters is even more uncertain where, due to lack of availability of anode effect performance, the median emission factors of reporters per technology is applied to non-reporters.

  • 13

    International Aluminium Institute | www.world-aluminium.org

    Benchmark Data The IAI Anode Effect Survey provides respondents with valuable benchmark information, allowing producers to judge their performance relative to others operating with similar technology. The benchmark data are presented in this section in the form of cumulative probability graphs and calculated PFC emissions benchmark data as both cumulative probability and cumulative production graphs.

    The cumulative probability graphs show, on the horizontal axis, the benchmark parameter:

    PFC emissions per tonne of aluminium;

    Anode effect frequency (AEF);

    Anode effect duration (AED);

    Anode effect minutes per cell day (AEM) and

    Anode effect overvoltage (AEO).

    The vertical axes show the cumulative fraction of reporting facilities that perform at or below the level chosen on the vertical axis. For facilities reporting data from multiple potlines, a data point is shown for each potline.

    To illustrate how the graph in Figure 10 is interpreted consider, for example, the 0.5 point on the vertical axis, at which the HSS data point is 0.98 t CO2e/t Al. The interpretation is that 50% of all potlines/facilities reporting HSS anode effect data operate at or below 0.98 t CO2e/t Al. At 1.0 on the vertical axis the HSS point is 4.23 t CO2e/t Al. The interpretation is that all HSS facilities reported anode effect data that reflected PFC emissions performance at or below 4.23 t CO2e/t Al or, in other words, the maximum value calculated for HSS operators in 2012 was 4.23 t CO2e/t Al.

    PFC Emissions per Tonne of Aluminium The lowest PFC emissions per tonne of aluminium produced are produced by PFPB facilities, although with a wide range of performance. The VSS and HSS facilities show a similar distribution, but with higher average emissions factor. The highest PFC emissions per tonne of aluminium produced and the widest range in performance result from SWPB cells.

  • 14

    International Aluminium Institute | www.world-aluminium.org

    Figure 10 – PFC emissions (as CO2e per tonne Al) performance of reporters, benchmarked as cumulative fraction within technologies, 2012

    Figure 11 –PFC emissions performance of reporters (t CO2e/t Al), benchmarked as cumulative production within technologies, 2012

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    Note: SWPB outlier at 22.0 Mt Al is 16.7 t CO2e/t Al

  • 15

    International Aluminium Institute | www.world-aluminium.org

    Taking the 1990 reporting cohort and plotting it against 2012 data shows improvement both from existing facilities over this time but also, importantly, the positive contribution of new (predominantly PFPB) capacity added since 1990.

    Figure 12 - PFC emissions performance of reporters (t CO2e/t Al), benchmarked as cumulative production within technologies, 1990 & 2012

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  • 16

    International Aluminium Institute | www.world-aluminium.org

    Anode Effect Frequency & Duration The following graphs shows the distribution of anode effect frequency and duration data for reporting facilities in 2012. As can be expected from the greater degree of control capability of PFPB cells, this technology has the lowest AEF distribution of the five groups.

    Figure 13 - Average anode effect frequency of reporters benchmarked by technology type, 2012

    Figure 14 - Average anode effect duration of reporters benchmarked by technology type, 2012

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  • 17

    International Aluminium Institute | www.world-aluminium.org

    Anode Effect Minutes per Cell Day Anode Effect Minutes per Cell Day (AEM) are the product of anode effect frequency and duration and, for facilities employing the Slope Method. AEM relate directly to PFC emissions per tonne of aluminium produced through a slope factor that is either technology specific (IPCC Tier 2 methodology) or facility specific (Tier 3 methodology).

    Both PFPB and CWPB technologies have the same Tier 2 value for slope: 0.143 kg CF4/t Al per AEM. However, the IPCC Tier 2 slope parameter for SWPB, VSS and HSS technologies are considerably different. The slope value is highest for the SWPB technology group, 0.272 kg CF4/t Al per AEM. The comparable slope values for VSS and HSS are 0.092 and 0.099, respectively.

    Figure 15 - Average anode effect minutes per cell day of reporters benchmarked by technology type, 2012

    Anode Effect Overvoltage Figure 16 shows the benchmarking graph for anode effect overvoltage for PFPB cells operating with Rio Tinto Alcan AP technologies and which calculate PFC emissions from overvoltage process data. For these operators, the AEO parameter relates directly to anode effect related PFC emissions per tonne of aluminium produced.

    0.0

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    Anode Effect Minutes per Cell Day (minutes) CWPB & PFPB SWPB HSS VSS

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    International Aluminium Institute | www.world-aluminium.org

    Figure 16 - Average anode effect overvoltage of reporters benchmarked by technology type, 2012

    Positive overvoltage reporting now predominates over algebraic overvoltage reporting. The positive overvoltage should give a better correlation with PFC emissions per tonne of aluminium than algebraic overvoltage since algebraic overvoltage recording can result in subtractions of voltage during the anode effect treatment period that do not relate to PFC emissions.

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    0 5 10 15 20

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    Anode Effect Overvoltage (mV)

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    International Aluminium Institute | www.world-aluminium.org

    Appendix A – Facility Emissions Calculation Methodologies

    Slope Method The basic equations for calculation of PFC emission rates from facilities reporting anode effect frequency and duration are:

    and

    / where

    kilograms of emitted kilograms of emitted

    slope coefficient for

    / weight fraction of to

    While AEF and AED are reported data, the slope coefficient for CF4 can be either “facility specific” (IPCC Tier 3 methodology), or “technology specific” (IPCC Tier 2 methodology). The first of these options, Tier 3, is the more certain method for calculating emissions and involves use of a slope coefficient (and weight fraction) derived from direct measurement of PFC emissions at the facility. The Tier 2 method involves the use of slope coefficients that are an average of measurement data available in 2005 taken from facilities around the world within technology classes.

    Table 6 - Slope and overvoltage coefficients by technology, including uncertainty (Source: IPCC, 2006)

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    International Aluminium Institute | www.world-aluminium.org

    Participants in the Anode Effect Survey are asked to report if a facility-specific direct measurement of PFC emissions had been made and if a Tier 3 slope coefficient and weight fraction are available for calculating PFC emissions from the smelter. The remainder of the PFC emissions data are calculated using IPCC Tier 2 methodology with industry average coefficients.

    Overvoltage Method For smelters that report overvoltage data, the following equations are employed:

    100

    and /

    where

    kilograms of

    kilograms of

    overvoltage coefficient for current efficiency, expressed as %

    / weight fraction of to Again, a Tier 3 methodology applies a facility specific overvoltage coefficient and weight fraction, derived from on site PFC measurements and anode effect data and reported as part of the Survey return. Tier 2 calculations apply technology specific, average coefficients, which are outlined in the 2006 IPCC Guidelines for National Greenhouse Gas Inventories.

    Global Warming Potentials Carbon dioxide equivalent (CO2e) emissions for survey participants are calculated by multiplying the total tonnes of each PFC component gas by the Global Warming Potential (GWP) values reported in the IPCC Second Assessment ReportF3F (i.e. 6,500 for CF4 and 9,200 for C2F6):

    6500 9200 For benchmarking purposes (that is to say, comparing emissions performance between facilities of the same technology but with different levels of production), total (or “absolute”) CO2e emissions are divided by relevant aluminium production, to give an emission factor in tonnes of CO2e per tonne of aluminium produced:

    3 The IPCC Second Assessment Report GWP values are employed to maintain consistency with Kyoto Protocol conventions and Clean Development Mechanism (CDM) and Joint Implementation (JI) accounting. The latest data published by IPCC in the Fourth Assessment Report reports the CF4 GWP as 7,390 and the C2F6 GWP as 12,200.

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