IMPACT ASSESSMENT - DRAFT VERSION Implementing Directive 2009/125/EC of the European Parliament and of the Council with regard to Ecodesign requirements for Power, distribution and small transformers ISR-University of Coimbra 12 October 2012 Aníbal T. De Almeida Fernando Martins Bruno Santos EUROPEAN COMMISSION COMMISSION STAFF WORKING DOCUMENT Full Impact Assessment Accompanying the document Proposal for a Commission Regulation Implementing Directive 2009/125/EC of the European Parliament and of the Council with regard to Ecodesign requirements for Power, distribution and small transformers ii COMMISSION STAFF WORKING DOCUMENT Full Impact Assessment Accompanying the document Proposal for a Commission Regulation Implementing Directive 2009/125/EC of the European Parliament and of the Council with regard to Ecodesign requirements for Power, distribution and small transformers Lead DG: ENTR Associated DG: Other involved services: Table of contents List of Tables .................................................................................................................................... v List of Acronyms...............................................................................................................................vi Definitions ...................................................................................................................................... viii 1. 2. Procedural Issues and Consultation......................................................................................... 1 1.1. Organization and Timing .................................................................................................. 1 1.2. Impact Assessment Board................................................................................................ 2 1.3. Transparency of the Consultation Process ...................................................................... 2 1.4. Preliminary Results of Stakeholder Consultation ............................................................ 3 Problem Definition................................................................................................................... 4 2.1 Market and Regulatory Failures ............................................................................................ 4 2.2 Baseline Scenario ................................................................................................................. 10 2.2.1. Scope of Transformers Covered (VITO & BIOIS, 2011) ................................................ 11 2.2.2. Relevance of Product Group for Eco-design Implementing Measures ....................... 13 2.2.3. Market Structure ......................................................................................................... 14 2.2.4. Sales and Stock ............................................................................................................ 14 2.2.5. Definition of Base-cases............................................................................................... 16 2.3 Future Trends....................................................................................................................... 18 2.3.1 Energy Price Evolution .................................................................................................. 18 2.3.2 Aluminium vs. Copper in the Windings ........................................................................ 20 2.3.3. Grain Oriented Steel vs. Amorphous steel (Main Source (DoE, 2011)) ...................... 22 2.4 Policies and Measures supporting energy efficiency of distribution transformers in non-EU countries .................................................................................................................................... 24 2.5 Legal Basis for EU Action...................................................................................................... 27 4. Policy Options ........................................................................................................................ 29 4.1 Option 1: Baseline (BAU) ..................................................................................................... 29 4.2 Option 2: Self-regulation ..................................................................................................... 30 4.3 Option 3: Energy Labelling Only........................................................................................... 30 4.4 Option 4: Ecodesign MEPS Regulation on Transformers .................................................... 31 4.4.1 Definition of the Types of Energy-Using Products Covered ......................................... 32 4.4.2 Implementation of Ecodesign Requirements .............................................................. 32 4.5 Option 5: Energy Labelling + Ecodesign Requirements ....................................................... 33 5. Impact Analysis ...................................................................................................................... 35 i 5.1 Economic analysis .......................................................................................................... 39 5.1.1. Energy savings.............................................................................................................. 39 5.2 Administrative Costs ............................................................................................................ 42 5.3 Social impacts ...................................................................................................................... 42 5.4 Greenhouse gas emission reduction ................................................................................... 43 5.5 Technology, functionality and innovation .......................................................................... 44 5.6 Health and safety ................................................................................................................. 45 5.7 Uncertainties and Sensitivity Analysis ................................................................................ 45 5.7.1 Assumptions related to the load factors ...................................................................... 45 5.7.2 Assumptions related to the electricity tariff ................................................................. 53 6. Conclusions ............................................................................................................................ 60 6.1 Proposed Efficiency Levels Based and Sensitivity Analysis Results ................................... 60 6.2 General Conclusions ........................................................................................................... 61 7. Monitoring and Evaluation ........................................................................................................ 63 8. References ................................................................................................................................. 64 List of Annexes ................................................................................................................................... ANNEX 1: Minutes of Consultation Forum meeting ......................................................................... I ANNEX 2: Commission Staff Working Document ........................................................................... XI ANNEX 3: Structure of the methodology used for establishing the technical, environmental and economic analysis ........................................................................................................................ XXV ANNEX 4: Methodology to Calculate the Life Cycle Cost (LCC) ................................................... XXV ANNEX 5: Sensitive Analysis Tables ............................................................................................ XXXI ANNEX 6: Life Cycle Cost Shaded Diagram ............................................................................. XXXVIII ANNEX 7: Environmental Impacts (VITO & BIOIS, 2011) ............................................................ XXIII ANNEX 8: European Distribution Transformer Loss standards.................................................. XXXV ii List of Figures Figure 1 - Transformer efficiency and different losses for 75 kVA oil immersed transformer (VITO & BIOIS, 2011). ................................................................................................................................. 5 Figure 2 - Transformer efficiency for different classes of 400 kVA oil immersed transformers (D0Ck, B0CK, A0Ck (top), (VITO & BIOIS, 2011). .............................................................................. 5 Figure 3 - Policy model for the distribution transformer market (SEEEDT, 2008)......................... 10 Figure 4 - Half-yearly electricity prices excluding taxes for Industrial consumers (new methodology from 2007 onwards) *including former GDR from 1991 (based on EUROSTAT data). ....................................................................................................................................................... 18 Figure 5 - Evolution of electricity price (€/kWh) in European Union (27 countries) – (based on EUROSTAT data)............................................................................................................................. 19 Figure 6 - Evolution of the price of Aluminium and Copper. ......................................................... 20 Figure 7 - Average Annual Prices for Specialty Steels in the US (2010$/lb, note: SA1 is finished core) (DoE, 2011) . ......................................................................................................................... 23 Figure 8 - Weighted sound power level at 60 Hz as a function of operating induction on SA1 amorphous material core and M3 silicon steel-based core (Azuma & Hasegawa, 2008). ............ 24 Figure 9 -Comparison of international transformer standards (VITO & BIOIS, 2011). .................. 26 Figure 10 - Market push and pull: How the different policy instruments can work together. Source: (SEEDT, 2007). ................................................................................................................... 34 Figure 11 – Energy Loss Scenarios Evolution 2005-2025 (TWh). ................................................. 38 Figure 12-Energy Evolution for MEPS Scenario (1st stage: 2014 & 2nd stage:2019). ................... 40 Figure 13 - Projected CO2 emissions per unit of electricity in the EU (adapted from (EURELECTRIC, 2010)). ................................................................................................................... 43 Figure 14 - Evolution of CO2 emissions between 2005 and 2025. ................................................. 43 Figure 15 - Annual energy losses for three different cases of load factor (min, base and max)BC1. ................................................................................................................................................ 46 Figure 16 -LCC for three different cases of load factor (min, base and max)- BC1 ....................... 46 Figure 17 - Annual energy losses for three different cases of load factor (min, base and max)BC2. ................................................................................................................................................ 47 Figure 18 - LCC for three different cases of load factor (min, base and max)- BC2. ..................... 47 Figure 19 - Annual energy losses for three different cases of load factor (min, base and max)BC3. ................................................................................................................................................ 48 Figure 20 - LCC for three different cases of load factor (min, base and max)- BC3. ..................... 48 Figure 21-Annual energy losses for three different cases of load factor (min, base and max)- BC4. ....................................................................................................................................................... 49 Figure 22-LCC for three different cases of load factor (min, base and max)- BC4. ....................... 49 Figure 23-Annual energy losses for three different cases of load factor (min, base and max)- BC5. ....................................................................................................................................................... 50 Figure 24-LCC for three different cases of load factor (min, base and max)- BC5. ....................... 50 Figure 25-Annual energy losses for three different cases of load factor (min, base and max)- BC6. ....................................................................................................................................................... 51 Figure 26-LCC for three different cases of load factor (min, base and max)- BC6. ....................... 51 iii Figure 27 - Annual energy losses for three different cases of load factor (min, base and max)BC7. ................................................................................................................................................ 52 Figure 28 - LCC for three different cases of load factor (min, base and max)- BC7 ...................... 52 Figure 29 - LCC for three different cases of electricity price (min, base and max)- BC1 ............... 54 Figure 30 - LCC for three different cases of electricity price (min, base and max)- BC2. .............. 54 Figure 31 - LCC for three different cases of electricity price (min, base and max)- BC3. .............. 55 Figure 32-LCC for three different cases of electricity price (min, base and max)- BC4. ................ 56 Figure 33-LCC for three different cases of electricity price (min, base and max)- BC5. ................ 57 Figure 34-LCC for three different cases of electricity price (min, base and max)- BC6. ................ 57 Figure 35 - LCC for three different cases of electricity price (min, base and max)- BC7. .............. 58 Figure 36 - Distribution of environmental impacts of BC 1 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). ................................................................................................. XXIV Figure 37 - Distribution of environmental impacts of BC 2 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). .................................................................................................. XXV Figure 38 - Distribution of environmental impacts of BC 3 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). ................................................................................................. XXVI Figure 39 - Distribution of environmental impacts of BC 4 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). ............................................................................................... XXVIII Figure 40 - Distribution of environmental impacts of BC 5 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). ................................................................................................. XXIX Figure 41 - Distribution of environmental impacts of BC 6 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). ................................................................................................. XXXI Figure 42 - Distribution of environmental impacts of BC 7 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). ............................................................................................... XXXIII iv List of Tables Table 1 - EU-27 distribution transformer losses (SEEDT, 2008). ..................................................... 6 Table 2- Barriers and obstacles towards increase energy efficiency of distribution transformers in the EU (Wuppertal Institute for Climate, Environment, Energy and SEEDT Partners, 2008). ......... 8 Table 3 - Summary of the market and stock data for 1990 – 2005 – 2020 (VITO & BIOIS, 2011). 15 Table 4 - Environmental impacts of the EU-27 stock in 2005 for all base-cases (VITO & BIOIS, 2011) . ............................................................................................................................................ 17 Table 5 - Summary of Life Cycle Cost Analysis (VITO & BIOIS, 2011). ........................................... 17 Table 6 - Copper and aluminium physical characteristics. ............................................................ 21 Table 7- Physical properties and prices of two pieces of copper and aluminium with similar electrical resistance. ...................................................................................................................... 21 Table 8 - Business As Usual (BAU) transformers scenario - No load losses at rated voltage and frequency (P0) & Load losses at rated current and reference temperature (Pk). .......... 36 Table 9 - Losses levels corresponding to the four different scenarios (BAU, LLCC, BAT, Intermediate /MEPS 2014 and MESP 2019). ................................................................................. 37 Table 10 - Impact Assessment Input (adapted from VITO 2011). ................................................. 39 Table 11 - Minimum Energy Performance Standard (MEPS) Adopt for 2014 and 2019. .............. 40 Table 12 - Energy consumption of existing transformers (old stock) and of new transformers (new stock installed after 2014), with the corresponding energy savings in TWh due to the transformers purchased in the period 2014-2025. ....................................................................... 41 Table 13 - Cumulative impacts and savings in the period 2014-2025. ......................................... 41 Table 14 - Cumulative Savings and Yearly savings in 2025 for Minimum Energy Performance Standard (MEPS) adopted in 2014 and 2019. .............................................................................. 41 Table 15 - Cumulative CO2 savings 2014-2025. ............................................................................. 44 Table 16 – CO2 Emissions and CO2 Savings (Mton) due to the transformers purchased in the period 2014-2025. ......................................................................................................................... 44 Table 17 – Annual Load factors used in this study. ....................................................................... 45 Table 18- Assumptions related to electricity tariff. ....................................................................... 53 Table 19- Losses levels corresponding to the four different scenarios (BAU, LLCC, BAT, Intermediate /MEPS 2014 and MESP 2019) and cumulative impacts and savings 2014-2025. .... 60 Table 20 - HD428/HD538 ........................................................................................................... XXXV Table 21 - EN 50464-1 ................................................................................................................ XXXV Table 22 - EN 50464-1 ............................................................................................................... XXXVI Table 23 - EN 50464-1 ............................................................................................................... XXXVI Table 24 - EN 50464-1 .............................................................................................................. XXXVII v List of Acronyms AC AF Al AM AMDT AMT BAT BAU BNAT BOM CENELEC CGO Cu DER DOE DSO EN EP ERP EU EuP GO GWP HV Hz IEC IEE k Kf LCA LCC LV MEEuP MEPS MV Paux PF Pk Po RES RoHS S SEEDT Si Alternating Current (Transformer) Availability Factor Aluminium Amorphous Metal Amorphous Metal Distribution Transformer Amorphous Metal Transformer Best Available Technology Business As Usual Best Not yet Available Technology Bill of Materials European Committee for Electrotechnical Standardization Cold rolled Grain-Oriented Steel Copper Distributed Energy Resources US Department of Energy Distribution System Operators European Norm Eutrophication Potential Energy Related Products European Union Energy using Products Grain Oriented Global Warming Potential High Voltage Hertz The International Electrotechnical Commission Intelligent Energy Europe Kilo (10³) Load form factor Life Cycle Assessment Life Cycle Cost Low Voltage Methodology for the Eco-design of Energy using Products Minimum Energy Performance Standard Medium Voltage Auxiliary losses Power factor Load losses at rated load No load losses Renewable Energy Sources Restriction of the use of certain Hazardous Substances in electrical and electronic equipment (transformer) apparent power Strategy for development and diffusion of Energy Efficient Distribution Transformers Silicon vi SME TCO small medium sized enterprise Total Cost of Ownership TOC TSO TWh V VA VITO Total Operational Cost Transmission System Operators TeraWatt hours Volt Volt-Ampere Flemish Institute for Technological Research Volatile Organic Compounds Waste Electrical and Electronic Equipment Short-circuit impedance Load Factor VOC WEEE Z α vii Definitions 1. Liquid-immersed transformer means a transformer in which the magnetic circuit and windings are immersed in liquid; 2. Dry-type transformer means a transformer in which the magnetic circuit and windings are not immersed in an insulating liquid; 3. Pole mounted transformer means a transformer connected by open bushings suitable for outdoor service and designed to be mounted on the support structures of overhead power lines; 4. Winding refers to the assembly of turns forming an electrical circuit associated with one of the voltages assigned to the transformer; 5. High-voltage winding refers to the winding having the highest rated voltage; 6. Rated power (S) is a conventional value of apparent power assigned to a winding which, together with the rated voltage of the winding, determines its rated current; 7. Load factor means the ratio of energy supplied by a transformer during a given period of time to the energy it would have supplied if it had been operating at its maximum rated power for the same period of time; 8. Load loss (Pk) means the active power absorbed at rated frequency and reference temperature associated with a pair of windings when the rated current is flowing through the line terminal(s) of one of the windings and the terminals of the other windings are in short-circuit with any winding fitted with tappings connected to its principal tapping; 9. No load loss (Po) means the active power absorbed at rated frequency when the transformer is energised and the secondary circuit is open. The applied voltage is the rated voltage, and if the energized winding is fitted with a tapping, it is connected to its principal tapping. viii 1. Procedural Issues and Consultation 1.1.Organization and Timing This implementing measure is one of the priorities of the Action Plan on Energy Efficiency1, and is part of the 2008 Catalogue of actions to be adopted by the Commission for the year 20082. The proposed implementing measure is based on the Directive 2009/125/EC of the European Parliament and of the Council establishing a framework for the Commission, assisted by a regulatory committee to set Ecodesign requirements for energy-using products3, in the following abbreviated as "Ecodesign Directive". An energy-related product, or a group of energyrelated products, shall be covered by Ecodesign implementing measures, or by self-regulation (cf. criteria in Article 17), if the Ecodesign represents significant sales volumes, while having a significant environmental impact and significant improvement potential (Article 15). The structure and content of an Ecodesign implementing measure shall follow the provisions of the Ecodesign Directive (Annex VII). Article 16 provides the legal basis for the Commission to adopt implementing measures on this product category. Consultation of stakeholders is based on the Ecodesign Consultation Forum as foreseen in Article 18 of the Directive (see next section for details), including the consultation of stakeholders during the preparatory technical study44 on 6 July 2009, 19 May 2010 and 24 August 2010 in order to assist the Commission in analysing the likely impacts of the planned measures. Article 19 of the Directive 2009/125/EC5 foresees a regulatory procedure with scrutiny for the adoption of implementing measures. Subject to qualified majority support in the regulatory committee and after scrutiny of the European Parliament, the adoption of the measure by the Commission is planned by the very end of 2013. 1 COM(2006)545 final. COM(2008)11 final. 3 OJ L 285 of 31.10.2009, p. 10. 4 Technical/economic Ecodesign study on Distribution and power transformers was conducted on January 2009 – 9 February 2011 by an external consultant VITO (Belgic) in partnership with BIOIS (France): http://www.ecotransformer.org 5 OJ L 285 of 31.10.2009. 2 1 1.2. Impact Assessment Board The opinion of the Impact Assessment Board was given on (……………...). This impact assessment has been scrutinised by the Commission's Impact Assessment Board (IAB). In its opinion, the IAB concluded that IA report (………………..). This final version of the impact assessment report reflects its recommendations as follows: TO BE COMPLETED AFTER RELEASE OF THE FINAL VERSION OF IA STUDY 1.3. Transparency of the Consultation Process Expertise was gathered in particular through a study providing a technical, environmental and economic analysis (from here on referred to as "preparatory study"), carried out by a consortium of external consultants6 on behalf of the Commission's Directorate General for Enterprise and Industry (DG ENTR). The preparatory study followed the structure of the "MEEuP" Ecodesign methodology7 developed for the Commission's Directorate General for Enterprise and Industry (DG ENTR). MEEuP has been endorsed by stakeholders and is used by all Ecodesign preparatory studies. The preparatory study took into account input from all relevant stakeholders including manufacturers and their associations, environmental NGOs, consumer organizations, and EU Member State experts. Information on the preparatory study was made publicly available through a dedicated website 8 where interim results and further relevant materials were published regularly for timely stakeholder consultation and input. The study website was promoted on the Ecodesign-specific websites of DG TREN and DG ENTR. Open consultation meetings for directly affected stakeholders were organised on 6 July 2009, 19 May 2010 and 24 August 2010 for discussing and validating the preparatory results of the study. On 20 April 2012 the Meeting of the Ecodesign Consultation Forum took place in Brussels, in which the Commission Service's proposals, building on the results of the 6 EuP preparatory studies "Lot 2: Distribution and Power Transformers, by Paul Van Tichelen and Shailendra Mudgal, final report of 9 February, 2011; documentation available on the Ecodesign website of the Commission's Directorate General Energy and Transport http://ec.europa.eu/energy/demand/legislation/eco_design_en.htm. 7 "Methodology for the Ecodesign of Energy Using Products", Methodology Report, final of 28 November 2005, VHK, available on DG TREN and DG ENTR Ecodesign websites: http://ec.europa.eu/energy/demand/legislation/eco_design_en.htm and http://ec.europa.eu/enterprise/eco_design/index_en.htm. 8 Available on: http://www.ecotransformer.org/. 2 preparatory study9, were presented. Minutes of the Meeting of the Ecodesign Consultation Forum are annexed (Annex 1). 1.4.Preliminary Results of Stakeholder Consultation The positions of the main stakeholders, as expressed before, during and after the Consultation Forum meeting on 20 April 2012 as a reaction to the Commission services' working document can be summarised as follows: -The general approach to set mandatory minimum requirements in the framework of Ecodesign is largely supported by industry associations but the level of requirements and the timing were questioned. While industry preferred lower minimum energy efficiency levels with slower introduction of the measures, environmental NGOs and some Member States requested higher performance levels and faster implementation than proposed. Further details on these issues are given in Annex 1. 9 Available on DG TREN’s Ecodesign website: http://ec.europa.eu/energy/demand/legislation/eco_design_en.htm#consultation_forum. 3 2. Problem Definition 2.1 Market and Regulatory Failures The underlying challenge in the transformer market transformation can be summarised in the following way: technical solutions exist on the market leading to reduced energy consumption of transformers, but the market penetration of high efficient transformers is lower than it could be. As requested by Article 15 of the Ecodesign Directive, the preparatory study identified the relevant energy and environmental aspects associated with the improvement of efficiency levels. The analysis showed that the most significant factor for improving the environmental performance of the power, distribution and small transformers is the life cycle energy consumption, and in particular their electricity consumption in the use phase. Transformers run 24 hours/7 days, 365 days a year and have very long lifetimes of typically over 30 years, so energy consumption is a dominant factor in their environmental impact. Increased use of electronic equipment and other non-linear loads leads to increased harmonic circulating currents and hence further increasing the losses in transformers. Unbalanced loads in 3-phase systems are another user factor that increases losses with negative impacts on “real life” transformer performance. Lifetime is strongly influenced by the operating temperature (itself a function of the load and of the ambient temperature), and also on the type of insulation system used. The choice between the two dominant technologies (oil filled and dry transformers) is actually dictated by fire hazards and ecological impact issues. Transformer efficiency is mostly characterised by two factors – standing (magnetic) losses and load dependent (resistive) losses (see Figure 1), both of which need to be characterised separately in order to give total losses over a wide range of loads. 4 Figure 1 - Transformer efficiency and different losses for 75 kVA oil immersed transformer (VITO & BIOIS, 2011). Figure 2 - Transformer efficiency for different classes of 400 kVA oil immersed transformers (D0Ck, B0CK, A0Ck (top), (VITO & BIOIS, 2011). 5 A projected large increase in distributed generation will impact the design and sales of distribution transformers, in which reverse power flows can in some cases occur. Transformers are very often replaced before their technical end of life, since the load they have to serve increases steadily (e.g. in urban areas) or stepwise (e.g. Industrial plants) and may exceed the transformer capacity long before its lifetime. Because of the long transformer lifetime, the installation of inefficient products will have an adverse environmental impact for a long time, and low stock rotation will make the impact of the ecodesign measures to take a long time to reach the full potential. The European distribution transformer fleet and market is still largely dominated by traditional technology. The average distribution transformers’ operating efficiency in Europe is 98.38% (VITO, 2011). Total losses of transformers in the distribution network are substantial and sum up to 38 TWh/year in EU-27, as shown in Table 1. Table 1 - EU-27 distribution transformer losses (SEEDT, 2008). The power transformer losses are 55 TWh, whereas the losses of small industry transformers are only 0.4 TWh (VITO & BIOIS, 2011). The distribution transformer market has been characterised by an emphasis on first cost and reduced concerns with operating cost, largely because of the split incentives between purchasers of equipment on the one hand, and owners/operators and users on the other. Additionally, the cost of transmission and distribution losses are passed on to consumers and the electricity distribution utilities who are responsible for purchasing a large number of 6 transformers are not motivated to invest in more efficient distribution transformers. In small industries the restricted capital availability and short term perspective also favour low initial cost solutions. Other relevant market barriers are existing long term contracts for supplying equipment, products already held in storage as spares and consulting engineers who use previous design specifications. Decisions based on these criteria can be rational from the perspective of the individual decision-maker but may incur higher societal costs. The utility market has historically been more concerned with minimizing lifetime owning costs, but changes in the structure of the electricity industry are changing the basis of distribution network asset management, in a way that is less conducive to the selection of energy efficient transformers. Even if the EU has produced an impressive number of energy policy measures on energy efficiency and CO2 reductions over the last ten years, an integrated framework to accelerate the use of energy-efficient transformers and to support a respective high quality European industry sector still does not exist. In general less effort has been made in the energy efficiency supply side, namely electricity distribution grid losses which are often neglected when talking about increasing energy efficiency. Due to the current regulatory framework in most of the EU-27 countries, only part of the electricity savings potential of energy-efficient distribution transformers is economically attractive for an electricity distribution company. Therefore, existing disincentives in regulatory schemes should be removed, reporting on transformers and distribution losses should be strengthened, and additional incentives should be introduced. Table 2 gives an overview on the main barriers and obstacles, that the different market stakeholders face. 7 Table 2- Barriers and obstacles towards increase energy efficiency of distribution transformers in the EU (Wuppertal Institute for Climate, Environment, Energy and SEEDT Partners, 2008). Based on the analysis of the existing European framework of national policies and measures and of the barriers and obstacles the different market actors are facing, the following list of policy instruments that might be applicable to foster energy efficiency of transformers, were considered: 8 Lack of knowledge is a significant barrier to the purchase of energy-efficient transformers. Labelling overcomes the information gap, by providing the purchaser with key criteria for the purchasing decision. Even if the final user is not the purchaser, the performance visibility acts as deterrent for the purchaser of the equipment. A labelling system that indicated the efficiency of transformers under specific load profiles would cause a significant movement in the market promoting a healthy competition among manufacturers. While there are obvious difficulties in creating a labelling system for transformers, given the variability of losses depending upon application, it is possible to develop a labelling system that in most instances provides the user with appropriate guidance. The mandatory MEPS option would address the key market barriers, by removing inefficient products from the market and by forcing investment in more efficient products. Finally, dynamic standards will give a signal to suppliers in which direction the market will develop. Figure 3 gives an idea how these policies and measures might address the different market actors to overcome the existing barriers and obstacles in the market ( (Wuppertal Institute for Climate, Environment, Energy and SEEDT Partners, 2008); (UNEP & International Copper Association Southest Asia Ltd., 2011); (AEA Technology, 2011)). 9 Figure 3 - Policy model for the distribution transformer market (SEEEDT, 2008). 2.2 Baseline Scenario The preparatory study for power, distribution and small transformers provided a technical, environmental and economic analysis of different technologies and efficiency levels. The study provided, amongst others, the following key elements: The scope of power, distribution and small transformers in detail by analysing further types and functionalities; The annual sales plus sales expectations up to 2020, the typical product life, and the installed base (“stock”) and definition of typical or average products (referred to as base cases); The bill of materials, weight, packaging etc. in order to evaluate the life cycle environmental impact of each transformers categories; Description of technologies yielding reduced electricity consumption and the additional costs for applying them compared to the current “market average” (base case). 10 Potential trade-offs between electricity consumption and material related environmental impacts. The structure of the methodology of the technical, environmental and economic analysis is displayed in Annex 3. The following sections describe in more detail the inputs used to define the baseline scenario for calculating future economical and environmental impacts. 2.2.1. Scope of Transformers Covered (VITO & BIOIS, 2011) The scope was decided on the basis of the Ecodesign Directive Articles 15 and 1610. The scope and product categorising were refined during the preparatory study together with stakeholders based on functional approach11. The definitions used in the impact assessment report are the same definitions used during the preparatory study, for the products select in the base-case scenario, as follows: 1. MV/LV Distribution transformers installed by DSO refer to any transformer that takes voltage from a primary distribution circuit and “steps down” or reduces it to a secondary distribution circuit or a consumer‘s service circuit at e.g. 400 VAC or 230 VAC with an input voltage of at least 1.1 kV. Distribution transformers can vary in size, with the most common ranging from 50 kVA to 2.5 MVA, with an input voltage between 1.1 and 36 kV. (EN 50464-1). Distribution transformers are operated by the DSO (Distribution System Operator) or Utilities. Sometimes these transformers are also referred as Utility transformers. Those transformers are three phase transformers. International standards are developed within IEC/TC 14 and CENELEC CLC TC 14. Please note that a more specific parameter is the MV or LV rated voltage. In general the European continent uses three phase transformers and single phase transformers are not generally used in Europe. 2. DER LV/MV connecting transformers are used to connect Distributed Energy Resources (DER) to the distribution grid, e.g.: wind turbines, photovoltaic, fuel cells. They might be designed with higher rated power than Distribution transformer (especially for wind turbines). Those transformers might also be optimized for a particular load profile and shape for integration (e.g. wind turbine). International standards are developed within IEC/TC 14 and standard IEC 60076-16 is in progress. 10 11 In particular Point 2 of Article 16. Ecodesign Directive Article 15, Point 2(ii). 11 3. MV/LV distribution transformers by non DSO (industry, ...) are used by the industry to purchase electricity at high voltage (HV) or medium voltage (MV) grid and step it down for use on site at Low Voltage (230/400 VAC). The size of industrial transformers is higher compared to distribution transformers. These transformers connect to the DSO. Also the tertiary sector (e.g. large retailer stores, hospitals, office buildings...) frequently installs these transformers. They range from 100 kVA until 4 MVA. Please note that smaller industrial consumers are connected to the distribution grid. International standards are developed within IEC/TC 14 and CENELEC CLC TC 14. Sometimes these transformers are also referred as Industry transformers. 4. Power transformers installed by TSO (DSO) or power plant owner refer to those transformers used between the generator and the distribution circuits and are usually rated at 5 to 1500 MVA or even higher, with an input voltage mostly above 36kV. They are used in the MV and/or HV electrical grid. It ranges from the maximum size of 2 large distribution transformers (i.e. 5 MVA) until the largest power plant (about 500 MVA). Power transformers are available for step-up operation, primarily used at the generator and referred to as generator step-up transformers, and for step-down operation, mainly used to feed distribution circuits. Power transformers are operated by the TSO (Transmission System Operator) or the generator (power plant owner). International standards are developed within IEC/TC 14. Sometimes these transformers are also referred as Transmission system transformers. 5. General purpose small power transformer means a transformer designed for use in electricity distribution grids with rated power from 1 up to 100 kVA and with a highest voltage for equipment not exceeding 1 kV, specifically designed or marketed for electrical power distribution. These are in general smaller transformers used in industrial LV electricity distribution. Identified relevant categories are: i. Separating transformer: Is a transformer that has primary and secondary windings electrically isolated by means of basic insulation, so as to limit, in the circuit fed by the secondary winding, the risks in the event of accidental simultaneous contact with earth and live parts. Typical size for three phase transformers is from 1 kVA up to 63 kVA. Please not that this is not common practice in industry and they are only used in cases of strong safety and availability requirements. ii. Isolating transformer: Is a separating transformer that has primary and secondary windings electrically isolated by means of double or 12 reinforced insulation. Frequent applications are a change of earthing system or a critical load protection in distorted systems. Typical size for these three phase transformers is from 1 kVA up to 63 kVA. Please note that this is not common practice in industry and they are only used in cases of severe electromagnetic compatibility requirements (e.g. also in medical equipment). Exemptions The draft Regulation does not apply to certain categories of small and special transformers such as: transformers which are not power transformers according to the definition given in EN 60076-1; single-phase transformers with rated power less than 1 kVA and three-phase transformers less than 5 kVA; instrument transformers; transformers for static convertors; traction transformers mounted on rolling stock; starting transformers; testing transformers; welding transformers. 2.2.2. Relevance of Product Group for Eco-design Implementing Measures As requested by Article 1512 of the Ecodesign Directive, the preparatory study identified that the all the covered transformers fulfill the criteria for setting ecodesign requirements because they: (1) Have a significant economical and environmental impact within the Community; (2) Present significant potential for improvement without entailing excessive costs; (3) Are not addressed properly by market forces; (4) Are not sufficiently addressed by other relevant Community legislation. 12 Art. 15, par. 2, sub a, of the Energy-related-Products Directive 2009/125/EC. 13 2.2.3. Market Structure The main European industry players for the distribution and power transformers are big international groups like ABB, Siemens, Areva, Schneider Electric, and some large/medium size companies like Cotradis, Efacec, Pauwels, SGB/Smit and Transfix. Transformer manufacturers from outside the EU include GE, Hitachi (Japan) and Vijai (India). Their respective material suppliers for winding wires and foil are a multitude of European and non-European companies and for electrical steel. For Grain Oriented electrical steel there are 4 suppliers in the EU (ThyssenKrupp Electrical Steel, Orb Electrical Steels, ArcelorMittal Frydek Mistek, Stalprodukt) and 8 producers outside the EU (NLMK/Russia, Nippon Steel/JP, JFE/JP, AK Steel/USA, ATI/USA, Baosteel/CHN, Wisco/CHN, Anshan/CHN, Posco/S. Korea), ArcelorMittal Inox/Brazil). Nevertheless, SMEs are also active in transformer production, especially for niche smaller industrial applications transformers. Today, amorphous steel transformers are manufactured in significant quantities by American, Asian and Indian companies, such as Hitachi, Zhixin and Kotsons. In Europe investments in amorphous steel transformers equipment are likely to increase. Transformers for industrial applications are most often sold and installed by SMEs in a B2B market and in some cases SMEs have service contracts with utilities for installation. They are not subject to any public tender. T&D Europe is the representative of the European Transformer Manufacturers, regrouping the Austrian, Belgian, British, French, German, Italian, Spanish, Portuguese, Netherlands and Turkish’s National Associations. Smaller industrial transformers are mainly produced by European SMEs. It is a niche market and clients often directly order with the manufacturer. It is estimated that there should be about 50 SMEs active in production; often these companies have only a few employees. 2.2.4. Sales and Stock The EU statistics and figures from the EU transformer industry (T&D Europe), show that the production/sales figures for distribution, industry and power transformers comply with the eligibility criterion from the Ecodesign Directive, viz. more than 200000 units sold per year and smaller industrial transformer sales was estimated at about 75000 units per year. As a consequence, for the total figure of distribution and power transformers there should be no 14 doubt that the eligibility criterion (Art. 15, par. 2, sub a, of the Energy-related-Products Directive 2009/125/EC) is met as annual sales is well above 200000 units. Moreover, this is certainly the case when the ‘unit‘ is defined as the ‘functional unit‘ used within this study being 1 kVA as shown in Table 3. Distribution transformers represent the largest share of both the stock and sales. Table 3 - Summary of the market and stock data for 1990 – 2005 – 2020 (VITO & BIOIS, 2011). Stock Transformer type Smaller Industrial Transformers MV/LV Distribution transformer DER LV/MV transformers Industry MV/LV oil transformer Industry MV/LV dry transformer Power transfomer Phase S type New installed sales 199020052005 2020 Replacement sales Total sales Total sales 19902005 20052020 1990 2005 2020 % p.a. % p.a. % p.a. units p.a. units p.a. units p.a. 0 10 10 10 750000 750000 75000 1,9 1,4 2,50 4,40 3,90 119.438 140.400 173,891 89 34 10,5 4,00 38,00 14,50 94 2,900 12,967 800 991 1,9 1,4 4,00 5,90 5,40 35.590 43,200 53,505 128 170 211 1,9 1,4 3,33 5,23 4,73 6,708 8,047 9,966 100000 49 64,35 80 1,9 1,4 3,33 5,23 4,73 2,539 3,046 3,772 100000 0,49 0,65 0.81 1,9 1,4 3,33 5,23 4,73 26 31 38 1990 2005 2020 KVA K units K units K units % p.a. % p.a. 16 750 750 750 0 250 2,714 3,600 4.459 2000 0,25 20 630 603 800 The population of distribution transformers in Europe is about 4,5 million units which about 3,6 million of these units are owned by electricity distribution companies. On average, in recent years, about 137.000 distribution transformers (MV/LV) have been sold annually in Europe. Together with small transformers below 25 kVA and power transformers > 20MVA, the number of transformers sold in Europe per year exceeds the threshold of 200.000 pieces set by the Ecodesign Directive. Almost all MV/LV distribution transformers are oil-immersed. For industry, transformers about 80% are oil-immersed transformers. From Table 3 it is can be seen that utilities operate at lower ratings, while industry and particularly dry type transformers have on average much higher ratings. The lower rating of utilities can be explained by transformers that are installed in residential and rural areas. The average rating of power transformers is about 100 MVA. This figure is reported as the average rating for power transformers by the sector organisation (members of T&D Europe, 04/06/2009). This does not mean that values corresponds to the most sold transformer, but it is 15 in between the product range, and it is also the borderline between the so-called medium and large power transformers. In some reports from electricity network operators (France and Belgium) the average ratings of a power transformer seems to be higher, at about 180 MVA per unit. Based on the wind turbines installed capacity by in 2005 (about 34 GW) and an average installed capacity of 2000 kVA (members of T&D Europe, 04/06/2009), the installed capacity is estimated to amount about 20 000 units (LOT 2 – Preparatory study, VITO, 2011; SEEDT, 2008). The numbers in the preparatory study for DER transformers seem to have largely underestimated the market. It must emphasized the very large growth of photovoltaic (PV) distributed generation in recent years (2005 to 2012). In Germany the installed capacity of 24 GW is approaching the wind power capacity. In Italy PV generation is already larger than wind power. Importations of transformers far outweigh by number the EU-27 production. For the years 2004 – 2007, imports exceed production by an average of 6.18 million units and a ratio of 9.23 import to production units. However, the opposite happens in terms of monetary value. The value of production over the 2004-2007 period is €3.28 billion far greater than import value, which is a produced to imported ratio of 13.6. 2.2.5. Definition of Base-cases The number of base-cases defined in the preparatory study was small enough to enable a simplified analysis of the market but large enough to deal with the technological spectrum of transformers. Based on the European market analysis, seven base-cases were defined: BC 1 – Distribution Transformer (400kVA); BC 2 – Industry Transformer: Oil-immersed (1MV); BC 3 – Industry Transformer: Dry-type (1.25MVA); BC 4 – Power Transformer (100MVA, primary voltage 132kV, secondary voltage 33kV); BC 5 – DER Transformer : Oil-immersed (2MVA); BC 6 – DER transformer : Dry-type (2MVA); BC 7 – Separation/Isolation Transformer (16kVA). Despite the small number of power transformers in stock, these transformers are responsible for about half of the overall impacts of the whole market of power and distribution 16 transformers in EU (see Table 4). DER transformers still represent a very small share of the overall environmental impacts but it is expected to grow in the near future because of the rising stock of this type of transformer. Table 4 - Environmental impacts of the EU-27 stock in 2005 for all base-cases (VITO & BIOIS, 2011) . Environmental Impact Total Energy [PJ] Of which electricity [TWh] Waste, hazardous/ incinerated [kton] BC1 199 17,9 41,9 BC2 151 13,8 24,7 BC3 47,3 4,36 2,38 Greenhouse Gases [Mt Co2 eq.] Volatile Organic Compounds [kt] Heavy Metals [ton Ni eq.] Particulate Matter [kt] 8,8 0,15 5,8 6,6 6,7 0,09 4,1 3,9 Eutrophication [kt Po4] 0,049 0,026 BC4 BC5 BC6 591 2,6 10,6 55,0 0,24 0,96 61,7 0,40 0,52 Emissions to air 2,1 25,9 0,12 0,48 0,02 0,31 0,002 0,005 0,95 13,1 0,07 0,22 0,63 9,3 0,06 0,20 Emissions to water 0,015 0,06 0,00 0,003 BC7 4,6 0,38 0,09 0,21 0,004 0,25 0,39 0,001 In general, the share of electricity in the Life Cycle Cost (LCC) analysis is significant: from 62% for distribution transformer up to 86% for DER dry-type transformers. Separation and isolation transformers have a larger share related for the product price (77%) because of their lower operating hours (lower availability factor and their shorter lifetime). Of the total consumer expenditure in 2005, electricity represents 72% of the global amount of money, estimated at 7 453 million Euros. Half of this annual expenditure is due to power transformers, which are much more expensive than the other types of transformers (see table below). Table 5 - Summary of Life Cycle Cost Analysis (VITO & BIOIS, 2011). Item EU-27 sales [units] Share of the EU-27 sales Product Price [M €] Electricity [M €] Total [M €] BC1 140.400 BC2 43.200 BC3 8.047 BC4 1.802 BC5 420 BC6 1.680 BC7 75.000 Total 270.549 51,9% 16,0% 3,0% 0,7% 0,2% 0,6% 27,7% 100% 860 1.385 2.244 472 1.068 1.540 131 338 470 1.297 4.277 5.574 8 71 79 47 284 331 101 30 131 2.916 7.453 10.369 17 2.3 Future Trends The following sections provide insights in the latest market trends which will be useful to identify potential base-cases and evaluating their improvement potential. 2.3.1 Energy Price Evolution Electricity prices vary significantly in EU. In each country also these prices are influenced by the consumer voltage/ contracted power level. For this study it is proposed to use the Eurostat average price of 0.0935 €/kWh for the industry sector for EU-27, in 2011, except for DER transformers and power transformers. In the case of DER transformers, it makes sense to use the average feed-in-tariff, which has been decreasing in the last 10 years. The value of 0.15 €/kWh will be used in this case. In the case of power transformers the value 0.05 €/kWh will be used as suggested by T&D Europe (T&D Europe position on Power Transformers, April 2012). For industrial consumers (with an annual electricity consumption between 500 and 2.000 megawatt hours (MWh)), electricity prices during the first half of 2011 were highest in Malta, Cyprus and Slovakia while the lowest prices were found in Estonia, Bulgaria and Finland: the price of electricity for industrial consumers in Malta was almost 3 times high as that in Estonia. In the second half of 2011, Cyprus had the highest increase in the electricity price, becoming the member state with the highest price of electricity, in general, almost half of the member states had an increase in electricity prices in the second half of 2011 (see Figure 4). Figure 4 - Half-yearly electricity prices excluding taxes for Industrial consumers (new methodology from 2007 onwards) *including former GDR from 1991 (based on EUROSTAT data). 18 Within the next three to seven years important developments are expected to take place in European wholesale electricity markets. These developments will influence the competitive market position of each country and the net exchange flows between the countries in Europe. Besides the expected demand growth and increasing fuel and CO2 prices, new investments in power generation capacity (including wind and solar energy) are foreseen as well as decommissioning of old power plants and nuclear power plants in Germany. In the coming years, the perspective for European Union is that energy prices will increase significantly, in 2020 it is possible that the price may achieve 1,5 higher than today, as shown in Figure 5. Figure 5 - Evolution of electricity price (€/kWh) in European Union (27 countries) – (based on EUROSTAT data). There is considerable uncertainty in projecting energy prices, and it is much more difficult to forecast prices for large energy users than for residential customers. While the effect of a low and high carbon price is captured, there is uncertainty in the increases projected for each of the components of the price. For example, wholesale electricity prices may be subject to upward pressure beyond what is included in the projections because of potential fuel supply competition (in particular the gas price), but the consideration of these factors was beyond the scope of this report. 19 2.3.2 Aluminium vs. Copper in the Windings Copper has traditionally been used in most transformers due its higher conductivity (for the same size of conductor), better mechanical properties (higher short circuit strength), and reliable electrical contact resistance. The amount of copper in the windings directly affects the load losses, having a direct impact in the manufacturing cost of the transformers. Copper prices have escalated rapidly in the last decade, due to fast growth in demand in emerging economies. Although copper has better conductivity than aluminium, copper is becoming much more expensive than aluminium and copper prices fluctuate widely trend to making cost forecasting difficult (see Figure 6), while aluminium is one of the most abundantly available metals in the earth. Figure 6 - Evolution of the price of Aluminium and Copper. Aluminium wiring was used quite extensively in residential homes from 1965 to 1976. It was also used in other applications such as commercial, industrial, and institutional buildings. After the late 1970's aluminium wire became unpopular, mainly due to poor electrical contacts leading reliability and safety (fire hazards) problems. It was not until the early 1990's that it started to be used again, although still not as much as copper. Aluminium wire in itself is safe, the main problem it is in the connections. Oxidation is the build up of a thin layer of aluminium oxide which creates a thin insulating layer increasing the electrical resistance of the connection and thus increasing heat build up - copper does oxidize but copper oxide does not act as an insulator and copper does not expand or contract as much when under load as does aluminium. When aluminium wiring was first used the 20 connection points on electrical equipment such as panel board breakers, receptacle and light switches etc. had copper terminations. Aluminium has different properties than copper and both react differently and expand and contract differently when under electrical load, which may cause the connections to become loose. When the connections become loose this can result in electric arc, arcing, oxidation and heat build up and finally the possibility of a fire through the ignition of surrounding combustibles such as the insulation on the wire, wall insulation or wallpaper in the area of the electrical box. A comparison of some of the properties of copper and aluminium are given in the following table. Table 6 - Copper and aluminium physical characteristics. 3 Density (g/cm ) Resistivity (Ω.m) Copper 8,90 1,72E-08 Aluminum 2,70 2,82E-08 Ratio Δ 3,30 6,10E-01 For a more concrete example, assume that both materials have a length of 1.000 m, and a cross section of 100 mm2 for the use of copper windings, then the resistance is 1,72E-01 Ω. Then, to ensure the same electrical resistance the following conditions are required for the aluminium conductor: Table 7- Physical properties and prices of two pieces of copper and aluminium with similar electrical resistance. Length (m) Resistance (Ω) Section (mm2) Weight (kg) Price (€/ton) – June 2012 Price Ratio Copper 1.000 1,72E-01 100 0,890 5.930,46 Aluminum 1.000 1,71E-01 164 0,443 1.505,32 Ratio Δ 0,61 2,01 3,94 7.91 For applications where weight is a concern, aluminium may be the better choice, approximately half the weight of copper. If space and size are a consideration, copper may be the better choice, i.e., about 40% less volume. Regarding the material price, for the same electrical resistance the aluminium is almost eight times cheaper than copper, and there is trend is to continue with this difference, as it can be seen in Figure 6. 21 2.3.3. Grain Oriented Steel vs. Amorphous steel (Main Source (DoE, 2011)) Grain Oriented Steels are used in most transformer cores and have experience significant improvements over the last decades. Amorphous core materials can slash the noload losses by 60-70%, and may play a very important role to build very high efficiency distribution transformers. In USA the share of amorphous core materials distribution transformers is close to 10% and in Japan about 30%. However, there are some concerns, which seem to being addressed by the market and by material improvement: The World market is largely dominated by a single player; Amorphous core materials are not yet made in the EU; A different manufacturing line is required to process the new material; Higher cost compared with Grain Oriented Steels models; Size and weight; Higher noise. Amorphous core material has been in existence for more than 35 years. Hitachi Metals is the only global supplier of the material. While Hitachi Metals is based in Japan, it also has a facility in the United States where amorphous metal is produced. The U.S. facility currently has three production lines, and can produce approximately 41,000 tons of amorphous steel per year. The Hitachi facility in Japan has two production lines, and can produce 30,000 tons per year. However, Hitachi is upgrading its Japanese facility to add two additional production lines, which will bring its capacity to 100,000 metric tons per year. In addition to Hitachi Metals, one other supplier is known to be producing amorphous metal commercially. A company based in China called Advanced Technology & Materials (AT&M) has production capacity of 40,000 tons per year. However, this company is not considered a global supplier, because it is not known to supply amorphous metal outside the Chinese market. Several other companies have attempted to produce amorphous metal in recent years. In Korea Posco has recently started the manufacturing of amorphous metals. Therefore, the current total global capacity for amorphous metal is over 140,000 tonnes per year, of which 40,000 tons are exclusively available to the Chinese marketplace. The remaining 100,000 tons are sold in the global marketplace. Compared to the 2.5 million of grain-oriented electrical steel produced in 2009, amorphous metal constitutes is less than six percent of the global supply for electrical steel. 22 Figure 7 illustrates the historical price trends of these steels from 2006 to 2010. Note that the amorphous material (SA1) represents the cost per pound of a finished core, while the other two steels represent the raw material price. DOE only considered the amorphous price from 2008 to 2010 because this is when North American amorphous core manufacturers began production. Figure 7 - Average Annual Prices for Specialty Steels in the US (2010$/lb, note: SA1 is finished core) (DoE, 2011) . The noise level of amorphous metals is similar to conventional steels up to 1.3 T, growing very substantially above that value, as shown in Figure 8. Amorphous metal cores are used up to 5MVA in oil filled transformers and 3 MVA in dry type transformers today. 23 Figure 8 - Weighted sound power level at 60 Hz as a function of operating induction on SA1 amorphous material core and M3 silicon steel-based core (Azuma & Hasegawa, 2008). 2.4 Policies and Measures supporting energy efficiency of distribution transformers in non-EU countries Across Europe, transformers are manufactured to individual national and European standards. Unlike many countries around the world, Europe has no mandatory standard on energy efficiency of distribution transformers. The two main documents which describe losses in transformers are: the European Standard EN 50464-1, which has superseded the harmonised document HD428 for oil cooled transformers, and the harmonised document HD538 for dry type transformers, which are still valid (or their various country equivalents, e.g., DIN, etc.), as it can be seen in Annex 8. Recently, a new EN Standard is on the way, the “Three-phase medium voltage transformer 50 Hz, with highest voltage for equipment not exceeding 36kV”, which will supersede EN 50541-1 and 50464-1 in the next twelve months. Efficiency standards outside Europe may be expressed in terms of electrical efficiency, at a certain load level, or in terms of maximum values for no-load and load losses. Some examples follow below: Australia “recalculated” the American 60 Hz efficiency NEMA TP-1 standard - which has never become mandatory in USA at federal level - to 50 Hz and also interpolated linearly 24 the efficiencies for ratings which are different from those used in the USA. New Zealand follows the Australian regulations for distribution transformers as a matter of policy. In China, the standards are regularly upgraded since 1999 with the Standard S7 and then S9 having been replaced by the current standard S11, which defines allowable levels for no-load and load losses slightly below Europe’s AC’ level (losses mix according to HD428 standard). S11 will soon be replaced by S13 which is expected to specify lower loss levels. The Indian Bureau of Energy Efficiency (BEE), classifies distribution transformers in the range from 25 up to 200 kVA into 5 categories from 1 Star (high loss) to 5 Stars (low loss). 5 Stars represents world class performance. 3 Stars is being proposed as a minimum efficiency standard, and is being widely followed by utilities. Japan has a different type of distribution system, with the last step of voltage transformation much closer to the consumer. The majority of units are pole mounted single phase transformers. The driver for setting up minimum efficiency standards was the Kyoto commitment. Transformers, together with 17 other categories of electrical equipment, should meet minimum efficiencies. In the case of transformers, the efficiency is defined at 40% load. Target average efficiency has been defined for the year 2006 (oil) or 2007 (dry type), based on the best products on the market in 2003 (Top Runner Programme). The standard is designed differently from other standards, with efficiencies for different products being described by equations. Mexico sets the minimum efficiencies at slightly less stringent levels, at 0.1% to 0.2% below NEMA TP-1 efficiency. As in Australia, the Mexican standard includes voluntary and mandatory elements. In USA, in 1997, the Oak Ridge National Laboratory performed extensive studies to determine whether energy conservation standards for distribution transformers would offer significant energy savings, be technically achievable and economically justified. The energy savings potential in the USA from switching to high efficient transformers was estimated to be 141 TWh cumulatively. One of the reasons for this high figure is the high number of distribution transformers (over 30 million) in the utility distribution networks in the US. To reduce these losses, the National Electrical Manufacturers Association (NEMA) created the TP1 standard which defines a minimum efficiency for dry and oilfilled type transformers in the range from 10 to 2500 kVA. This became the basis for the rule making process on minimum efficienct standards. NEMA TP-1 has been used as a guideline by Canada, Australia, New Zealand and (partially) Mexico. In USA it was 25 adopted by Massachusets, Minnesota, Wisconsin, New York, Vermont, California and Oregon. Subsequently, this standard was perceived as insufficiently demanding and, in 2006, the US Department of Energy (DoE) proposed a new standard. This proposal was a compromise between the less stringent TP-1 level and the least life cycle cost (LLCC) level, with the proposed loss levels set to represent one third of the improvement between TP-1 and LLCC. More recently new 2007 standard, closely based on the DoE proposal, has been introduced which will apply to all transformers manufactured for sale in the USA or imported into the USA on or after 2010. The requirement of the standard is very close to CC’ -30% or AoBk. In addition to this standard, distribution transformers are also a part of the broader EnergyStar labelling programme. EnergyStar is a voluntary programme that encourages the participating utilities to calculate the total cost of ownership of their transformers to base their purchasing decisions. A third programme in the US, set up by the Consortium for Energy Efficiency (CEE), aims to increase the awareness of the potential of efficient transformers in industry. It consists of a campaign to measure the efficiency of industrial transformers and to stimulate companies to upgrade their transformer park to the best available in the market. Canada follows TP-1 strictly but the mandatory levels apply only for dry type transformers. As far as oil transformers are concerned Canada has conducted an analysis of MEPS implementation potential and found that the great majority of Canadian oil distribution transformers already comply with NEMA TP-1 so the standard would have almost no influence on the market. Also Energy Star products are very actively promoted in Canada (SEEDT, 2008); (VITO & BIOIS, 2011). Figure 9 -Comparison of international transformer standards (VITO & BIOIS, 2011). 26 2.5 Legal Basis for EU Action The Ecodesign Directive and, more specifically, its Article 16 provides the legal basis for the Commission to adopt an implementing measure reducing energy consumption of transformers. 27 3. Objectives As laid out in Section 2, the preparatory study has confirmed that a large cost-effective potential for reducing electricity consumption of transformers exists. Further improvements of the environmental impacts are related to the total energy consumption and waste. The general objectives are therefore to develop a policy which corrects the regulatory and market failures, and whose general goals are: I.) Significant reduction of the environmental impact related to the energy use of transformers throughout the life cycle following Community environmental priorities, such as those set out in Decision 1600/2002/EC or in the Commissions European Climate Change Programme (ECCP) ; II.) Promote energy efficiency and contribute to the security of supply in the framework of the Community objective of saving 20% of the EU's energy consumption by 2020. The specific objectives are to: I.) Remove least efficient products from the market; II.) Promote market take-up of the most energy efficient transformers in the scope of the assessment; III.) Define policies and measures to promote the above mentioned market transformation, in such a way that are benefits to all key stakeholders . While aiming at these objectives, the Ecodesign Directive, Article 15 (5), requires that Ecodesign implementing measures also meet the following criteria: a) There shall be no significant negative impact on the functionality of the product, from the perspective of the user; b) Health, safety and the environment shall not be adversely affected; c) There shall be no significant negative impact on consumers in particular as regards the affordability and the life cycle cost of the product; d) There shall be no significant negative impact on industry’s competitiveness; e) In principle, the setting of an Ecodesign requirement shall not have the consequence of imposing proprietary technology on manufacturers; f) No excessive administrative burden shall be imposed on manufacturers. 28 4. Policy Options In order to address the objectives and meet the targets identified in Section 3 it is important that the energy losses of transformers are minimized in a cost-effective way and that the other relevant environmental parameters are addressed. The following policy options to improve energy efficiency of these appliances have been assessed in the following sessions. 4.1 Option 1: Baseline (BAU) This option would have the following implications: The regulatory and market failures would persist. The impact of this option is described in more detail in Section 2, as the Baseline scenario. Therefore the barriers for realizing the potentials to improve the environmental performance of transformers would persist (see Table 2); In the absence of EU action, It is to be expected that Member States may want to take individual (non-harmonised) action on transformers to speed up the increase in energy efficiency of appliances. This possibility is further reinforced due to the rapid introduction of minimum requirements in third countries (e.g. Australia, Canada, USA). Such action would hamper the functioning of the internal market and lead to high administrative burdens and costs for manufacturers, in contradiction to the goals of the Ecodesign Directive; There is a risk of competitive disadvantages, in particular for very price sensitive applications, for those manufacturers designing their products to high standards vis-àvis competitors not using technology leading to such low energy consumption; The specific mandate of the Legislator (Article 15.113) would not be respected despite the fact that all the criteria of Article 15.2 setting the rationale for an implementing measure are met. The "Business-as-usual" (BAU) scenario is based upon this option and provides the reference for comparison with other proposed scenarios. 13 Article 15.1 sets out the requirement for an implementing measure for products meeting the criteria listed under paragraph 2 (Article 15.2). 29 4.2 Option 2: Self-regulation Under Option 2, industry is expected to adopt measures to increase the energy efficiency of the transformers. However, so far no initiative for self-regulation on transformers has been brought forward by any industrial sector (refer to Table 2), so this Option is unlikely to be effective to meet the Directive’s objectives. The specific mandate of the Legislator (Article 15.1) would not be respected despite the fact that all criteria of Article 15.2 setting the rationale for an implementing measure are met. Therefore the option of voluntary agreements is discarded from further analysis. 4.3 Option 3: Energy Labelling Only A labelling system that indicates the efficiency of transformers under specific load profiles would assist this group of energy-using products considerably, and is likely to produce a significant movement in the market. While there are obvious difficulties in creating a labelling system for transformers, given the variability of losses depending upon application, in most instances it is possible to develop a labelling system that provides the user with appropriate guidance. The introduction of a labelling system also provides a framework from which future minimum standards may be derived (if deemed appropriate). ). The framework could also be used for financial incentives associated with efficiency programmes, should they be required at a national level. In an ideal case, the users of distribution transformers determine a specific loss combination for the transformer they want to purchase based on the specific circumstances (load characteristics) in which the transformer will be used, as well as on the transformer price and energy prices, with the objective to minimise life-cycle costs. This means that while in one situation, from an individual cost perspective, a transformer with very low load losses and medium no-load losses might be the optimal choice, in another situation a transformer with medium load losses and very low no-load losses might be preferred. Therefore, the following issues deserve to be analysed: If an energy label like the one that has been developed for household appliances in Europe, i. e. with energy efficiency classification from A to G, will be appropriate at all; If manufacturers will be just required to indicate the no-load and load losses clearly visible on the nameplate of the transformer, or, 30 if another approach has to be developed that may be more appropriate. Energy labelling pursuant to the Energy labelling Directive creates market transparency, fosters awareness of consumers and creates incentives for manufacturers for innovation. In general the two main objectives of labelling schemes are to increase the market penetration of energy efficient products by providing incentives for innovation and technology development, and to help consumers to make cost effective purchasing decision by addressing running costs. This option is however discarded for the following reasons: A labelling scheme alone does not ensure that cost effective improvement potentials are realised for all products on the market, implying that the full energy and cost savings potential is not captured. The speed of the market transformation is entirely determined by the voluntary take-up of labelled products. The market transformation due to the implementation of the labelling scheme will not be driven forward by the 'pushing' effect from Ecodesign requirements setting minimum energy efficiency thresholds. Member States could set minimum performance requirements individually, and the administrative burdens for manufacturers would be higher when compared with the burdens associated to Ecodesign requirements. A labelling scheme alone would not prevent the entering of low-efficiency transformers into the EU market as described in the section on ‘Market Failures’. The specific mandate of the Legislator (Article 15.1) would not be respected: all of the criteria listed in Article 15(2) giving grounds for an implementing measure are met. Consequently there is a high risk that market transformation towards high-efficient transformers would take place only very slowly at the corresponding detrimental impact on environment and life cycle cost for consumer. 4.4 Option 4: Ecodesign MEPS Regulation on Transformers This option aims at improving the environmental impact of transformers, i.e., either by setting maximum levels for load and no-load losses or defining minimum performance levels. This sub-section contains details of the rationale for the elements of the corresponding regulation, as listed in Annex VII of the Ecodesign framework directive. This option would achieve the following impacts: 31 Ensure cost-effective reduction of transformers losses and related CO2 mitigation; Correct market failures and ensure proper functioning of the internal market; Decrease the life-cycle cost of transformers for the consumer without reducing the profit margins of retails/producers; MEPS Regulation on Transformers allows the specific mandate of the Legislator to be respected and does not entail heavy administrative burdens for manufacturers or retailers. The following sub-options for the intensity of the measure are considered for comparative impact analysis: A. Least life cycle cost (LLCC), this option would include the setting of Ecodesign requirements for minimum energy efficiency implementing all LLCC options under the Ecodesign Directive; B. Best Available Technology (BAT), this option would include the setting of Ecodesign requirements for minimum energy efficiency implementing all BAT options under the Ecodesign Directive; C. Intermediate (2014 first stage MEPS) and 2019 second stage MEPS, this option would include the setting of Ecodesign MEPS requirements implementing Top Efficient level of EN 50464-1 for Tier 1 (2014) and LLCC for Tier 2 (2019). 4.4.1 Definition of the Types of Energy-Using Products Covered The devices covered by the Ecodesign measure on transformers are in line with the scope of the preparatory study and the Commission Staff Working Document and establishes the requirements related to transformers with a minimum power rating of 1kVA used in 50Hz electricity transmission and distribution networks and in consumers. 4.4.2 Implementation of Ecodesign Requirements According to the 2009/125/EC, the target levels for measures should be set at least life cycle cost (LLCC), which presumes that at some point, the price of the product increases so much with extra design options to save energy, that the life cycle costs (purchase price plus running costs) will start to rise again. The preparatory study has shown that the proposed level is cost-effective for the end user and can be achieved with current or expected state-of-the-art 32 technology. However, the cost of the measure for the transformer industry must be taken in due consideration, particularly if there is technological change in the manufacturing process. The Directive lists a set of criteria that need to be met when designing an implementing measure. However, the Article 15 of the Ecodesign Directive does not set the required criteria in any hierarchy14. 4.5 Option 5: Energy Labelling + Ecodesign Requirements This option combines the setting of minimum energy efficiency requirements with the introduction of a labelling scheme. Energy labelling of transformes provides purchasers and consumers with information about the energy consumption. This will help the purchaser/consumer to choose a transformer with lower losses, which will more cost-effective to operate. The main benefits of simultaneous introduction of minimum efficiency standards and energy labelling requirements are that: Labelling scheme is adapted to the levels of the ecodesign measure ensuring the label's long-term function as a market tool to drive up the transformers efficiency; Removal of the least efficient models from the market is guaranteed; Synergic impact of the pushing effect of the eco-design specific requirements and the pulling effect of a functioning labelling scale, as demonstrated on the basis of the qualitative but well experienced relation illustrated in Figure 10. This leads to long term improvement of stock efficiency (minimum efficiency requirements define a threshold that in practice will not be lowered in the future, only raised); Complies with the demand of stakeholders for a harmonisation and rationalisation of both measures. 14 However, it can be assumed that the criteria for a significant environmental impact precedes the criteria on indicative volume of 200.000 (e.g. if 10.000 commercial refrigerators consume ten times more than 10 million chargers, then there might be enough reason to base an implementing Regulation on the Art. 15.b even if in apparent conflict with Art. 15.a, provided that the criteria listed in Art. 15.c and d are fulfilled. 33 Figure 10 - Market push and pull: How the different policy instruments can work together. Source: (SEEDT, 2007). 34 5. Impact Analysis Given that options 1, 2 and 3 have been discarded in Section 4, this Section looks into the impacts of option 4 (option 5 has a similar impact). To this end an assessment of possible sub-options as regards the “intensity” of the measure — the combination of the levels of requirements and the timing for the levels pursuant to Article 15 (4f) of the Ecodesign Directive — is carried out. The assessment is done to follow the criteria set out in Article 15 (5a-5f) of the Ecodesign Directive, and also addresses the potential impacts on manufacturers. The aim is to find a balance between the quick realisation for achieving the appropriate level of ambition producing the associated benefits for the environment and the user (due to reduction of lifecycle costs) on the one hand, and on the other hand, the potential burdens related e.g. required re-design of equipment for achieving compliance with Ecodesign requirements, while avoiding negative impacts for the user, in particular as related to affordability and functionality. The methodology of the analysis is explained in Annex 3. The economic, environmental and social impacts are analysed and presented in a summary table at the end of the chapter followed by a brief discussion of the sensitivity to price changes (three levels minimum, base, maximum). The base case electricity price corresponds to average industrial electricity price for 2011 in EU27 (Eurostat). The starting point for impacts is the electricity (TWh) savings, which are disaggregated per seven base cases. Transformer lifetime ranges from 20 to 40 years or more, and savings figures are provided from 2005 data until 2025. Due to the long life time of transformers, further savings will be achieved after 2025. The preparatory study has shown that existing cost effective technical solutions allow for considerably lower electricity consumption levels for distribution and power transformers than the current market average. According to the different seven base cases of the preparatory study, the average transformer electricity consumption is associated with the lower efficiency level of technology sold in Europe, as indicated in Table 8. 35 Table 8 - Business As Usual (BAU) transformers scenario - No load losses at rated voltage and frequency (P0) & Load losses at rated current and reference temperature (Pk). No load losses at rated voltage and frequency (P0) Load losses at rated current and reference temperature (Pk) D0 E0 C0 41 kW E0 C0 110 W Ck Dk Bk 326 kW Ck Bk 750 W BC1 BC2 BC3 BC4 BC5 BC6 CB7 According to the Ecodesign Directive requirements on energy consumption in use, the aim of the analysis is to identify the least life-cycle cost (LLCC) for the end-user which is carried out (Annex 4). The BAT levels are based on the working document and on the comments from stakeholders. The preparatory study and additional input from stakeholders in the Consultation Forum has shown that the lowest achievable power consumption levels can be achieved by applying the best available transformers technology (BAT). New technologies, namely amorphous metal transformers were not included into the analysis due to the uncertainty on the large-scale availability of amorphous material and its market (Section 2.3.3). The Intermediate levels (possible MEPS in 2014) are derived from the top values in EN 50464-1 for distribution transformers. For power transformers a middle point was considered in the load losses between BAU and LLCC. For the no-load losses the LLCC value is equal to BAU, and the Intermediate value is the same. The simulation of more than 1000 design options of the different types of transformers (as showed in Annex 6) using the simplified LCC analysis (described in Annex 4) has shown that for distribution transformers, the Tier 1 level (2014) at A0Ak is a progressive intermediate stage, while Tier 2 level (2019) can be more ambitious to reach the LLCC point around A0-20%, Ak20%. This can be achieved by the manufactures using existing technology (e.g. high grade commercially available silicon electrical steel) and their existing manufacturing equipment. Table 9 shows the proposed MEPS levels for 2014 and 2019 for different transformer types. The MEPS in 2014 for distribution transformers are proposed to be at A0Ak level , and the MEPS at 2019 are proposed to be at A0-20%Ak-20% level. These levels are strictly based on LLCC levels for BC3, BC5 and BC6. For BC1 and BC2 the LLCC levels show very little variation for different efficiency levels (as shown for BC1 in Figure 16 and for BC2 in Figure 18). For load 36 factors above the base value and/or for electricity prices above the base value, the A0-20%Ak20% is also the LLCC. Since the trend of electricity prices is clearly upwards, as shown in Figure 5, the A0-20%Ak-20% level seems a robust choice for all types of distribution transformers. For power transformers, the MEPS for 2014 and considered at a level half-way between BAU and LLCC. In power transformers because of the high cost of improved models, the LLCC performance is significantly lower than the BAT, leading to modest savings. For small transformers the scope for improvement , as well as the savings potential, seems more limited. Therefore the MEPS at 2014 are set at BAU levels, with the 2019 MEPS based on the LLCC showing a significant improvement for the no-load losses. Table 9 - Losses levels corresponding to the four different scenarios (BAU, LLCC, BAT, Intermediate /MEPS 2014 and MESP 2019). P0Pk BAU LLCC BAT Intermediate MEPS 2014 MEPS 2019 BC1 D0Ck A0-15%Ak A0-20%Ak-20% A0Ak A0-20%Ak-20% BC2 E0Ck A0-15%Ak A0-20%Ak-20% A0Ak A0-20%Ak-20% BC3 C0Bk A0-20%Ak-20% A0-20%Ak-20% A0Ak A0-20%Ak-20% BC4 41-326 41-261 20-228 41-294 41-261 BC5 E0Ck A0-20%Ak-20% A0-20%Ak-20% A0Ak A0-20%Ak-20% BC6 C0Bk A0-20%Ak-20% A0-20%Ak-20% A0Ak A0-20%Ak-20% BC7 110-750 65-750 65-750 110-750 65-750 Figure 11 shows the evolution of the transformer energy consumption in the 4 scenarios with the introduction of MEPS in 2014, with different efficiency requirements. 37 Figure 11 – Energy Loss Scenarios Evolution 2005-2025 (TWh). 38 5.1 Economic analysis 5.1.1. Energy savings For the seven different base cases the key input data considered are presented in the following table. To identify the most attractive LLCC options for 2014 and 2019, three different levels of electrical power price and annual load factor (i.e., minimum, base and maximum values) were considered. The stock growth for different types of transformers ranges from 1.4% to 10.5%, depending on the type. The yearly sales is the sum of replacement units (stock/lifetime), plus the annual increase. For each type of transformer the preparatory study evaluated the price of the transformer as a function of the loss level. For the impact assessment Table 10 shows the key parameters used in the analysis. In some cases, different values were used for the load factor and for the electricity prices in relation to the preparatory study. The values used seem more realistic, but can be revised based on stakeholder comments. Table 10 - Impact Assessment Input (adapted from VITO 2011). INPUTS Lifetime (Years) Min Electricity rate Base (€/kWh) Max Discount rate Min Load Base Factor Max Load Form Factor EU Stock (2011) Stock Growth Classification Total Energy Losses (kWh/year) Product Price(€) Electricity cost (€) Life Cycle Cost (€) BC1 Distribution 40 0,10 0,15 0,30 1,073 2.451.074 D0Ck BC2 Industry OIL 25 0,0468€ 0,0935€ 0,1403€ BC3 Industry Dry 30 BC4 Power BC5 DER Oil BC6 DER Dry 30 25 25 0,035 0,075 € 0,05€ 0,15 € 0,075€ 0,225 € 4% 0,15 0,15 0,20 0,15 0,15 0,30 0,30 0,30 0,25 0,25 0,40 0,40 0,5 0,30 0,30 1,096 1,096 1,08 1,5 1,5 549.065 118.272 70.205 7.300 29.201 1,4% 1,5% 10,5% Baseline Transformer Technology (for unit) E0Ck C0Bk 41-326 E0Ck C0Bk BC7 Separation/ Isolation 20 0,0468€ 0,0935€ 0,1403€ 0,15 0,25 0,35 1,096 750.000 0% 110-750 7.859 30.091 39.727 724.886 59.093 62.415 5.738 6.334€ 14.544€ 20.877€ 10.239€ 43.953€ 54.192€ 27.378€ 64.231€ 91.609€ 743.886€ 839.561€ 1.773.011€ 18.248€ 230.791€ 249.039€ 28.191€ 146.258€ 174.449€ 1.153€ 7.827€ 8.980€ 39 As shown in Table 11 and Table 12 to Table 14, the power consumption levels start to drop with the first MEPS stage (2014). These savings are provided by readily available technologies (Top levels in EN 50464-1) which lead to a considerable reduction of the transformers life-cycle cost from the end-user perspective. Additional reduction is achieved with the second MEPS stage (2019). With the natural evolution of technology and market, the 2019 proposed scenario will be quite acceptable and feasible. Table 11 - Minimum Energy Performance Standard (MEPS) Adopt for 2014 and 2019. BC1 BC2 BC3 BC4 BC5 BC6 BC7 BAU MEPS 2014 MEPS 2019 P0PK D0Ck E0Ck C0Bk 41-326 E0Ck C0Bk 110-750 P0PK A0Ak A0Ak A0Ak 41-294 A0Ak A0Ak 110-750 P0PK A0-20%Ak-20% A0-20%Ak-20% A0-20%Ak-20% 41-261 A0-20%Ak-20% A0-20%Ak-20% 65-750 Figure 12-Energy Evolution for MEPS Scenario (1st stage: 2014 & 2nd stage:2019). 40 Table 12 - Energy consumption of existing transformers (old stock) and of new transformers (new stock installed after 2014), with the corresponding energy savings in TWh due to the transformers purchased in the period 2014-2025. 2014 2015 2016 2017 2018 2019 2020 2021 2022 2023 2024 2025 BAU 98,7 100,3 102,1 103,9 105,7 107,6 109,6 111,7 113,9 116,1 118,4 120,9 Old Stock 98,7 95,5 92,2 88,9 85,6 82,2 78,6 74,9 71,2 67,4 63,5 59,6 1StMEPS - 3,9 7,8 11,9 16,0 20,2 20,2 20,2 20,2 20,2 20,2 20,2 2ndMEPS Annual Savings - - - - - - 3,9 7,9 11,9 16,1 20,4 24,8 0,00 1,00 2,02 3,07 4,14 5,25 6,94 8,68 10,48 12,34 14,26 16,25 Table 13 - Cumulative impacts and savings in the period 2014-2025. Scenario Savings MEPS 2014* 46,98 TWh MEPS 2019** 37,45 TWh TOTAL 84,43 TWh *Savings due to the transformers purchased in the period 2014-2018 **Savings due to the transformers purchased in the period 2019-2025 Savings CO2 12,5 Mton 9,3 Mton 21,8 Mton Table 14 - Cumulative Savings and Yearly savings in 2025 for Minimum Energy Performance Standard (MEPS) adopted in 2014 and 2019. MEPS2014 MEPS2019 Total Yearly Savings in 2025 ∆%* BC1 BC2 BC3 BC4 BC5 BC6 BC7 14,79 TWh 16,59 TWh 2,99 TWh 6,00 TWh 1,84 TWh 4,77 TWh 0,00 TWh 9,58 TWh 10,56 TWh 2,55 TWh 6,00 TWh 1,82 TWh 5,88 TWh 1,06 TWh 24,37 TWh 27,15 TWh 5,54 TWh 12,00 TWh 3,66 TWh 10,65 TWh 1,06 TWh 4,42 TWh 4,90 TWh 1,07 TWh 2,40 TWh 0,78 TWh 2,37 TWh 0,30 TWh 5,7% 8,2% 5,3% 1,1% 22,7% 15,6% 2,7% Total 46,98 TWh 37,45 TWh 84,43 TWh 16,25 TWh 4,0% *Note: Percentage of savings in 2025 relatively to the BAU scenario. The overall impact is limited because of the very slow rotation of the transformer stock, with the exception of distribution generation transformers. The impact for power transformers is very small since the LLCC losses (with the assumed transformer costs, load factor and electricity prices) are similar to BAU. Small transformer also present a small potential because of their much lower energy consumption (TWh value). 41 5.2 Administrative Costs The form of the legislation is a regulation which is directly applicable in all Member States. This ensures no costs for national administrations for transposition of the implementing legislation into national legislation. The costs for carrying out the verification procedure for market surveillance purposes depends mainly on the product price (assuming a purchase by public authority), and the possible need for a second test on a sample of three additional products in the case that the power consumption levels established in the first test are excessive. It is to be expected that a product is tested not only for its conformity with Ecodesign requirements, but also with further applicable requirements, and the part of the costs required for testing the energy losses of a transformer is expected to be acceptable because the measurement on transformer efficiency is generally used. 5.3 Social impacts Social impacts due to potential Implementing Measures may affect employment of skilled and semi-skilled workforce, if Europe loses market share. The production of high efficiency units should lead to a more competitive EU industry in the World market. Higher efficiency units are more expensive leading to higher turnover and potentially higher profitability of the EU transformer industry. Businesses may decide to leave the marketplace depending on the compliance costs and this could affect employment negatively if businesses leave the EU. Of concern among stakeholders is the use of amorphous technology in production of the transformer cores, of which there is currently no production capacity within Europe, although this situation may change if the demand picks up. However, the expected performance requirements in the shortmedium term are not expected to mandate efficiency levels that are attainable only with amorphous metal technology (required to go beyond A0-20%), thus still allowing for manufacturers of high performance grain oriented steel to meet the requirements. It is foreseen that more specialised processes and manufacturing equipment may be needed to produce more efficient products. This could result in training requirements and a more skilled workforce. 42 5.4 Greenhouse gas emission reduction The accumulated electricity savings and the reduction of CO2 emissions depend on the timing of the first and of the second stage of the regulatory measures. Qualitatively, the sooner the requirements become effective and the shorter the delay between first and second stage, the higher the accumulated electricity savings and the related CO2 emissions. The accumulated CO2 savings by 2020 and 2025 are shown in the graph and in the table below. Figure 13 - Projected CO2 emissions per unit of electricity in the EU (adapted from (EURELECTRIC, 2010)). The estimated cumulative CO2 emission savings between 2014 and 2025 will be about 21,8 Mton. Figure 14 - Evolution of CO2 emissions between 2005 and 2025. 43 The significant decrease of the carbon emissions, shown in Figure 14 and Table 16, is a result of the combined effect of the transformer MEPS, as well as of the progressive decarbonisation of the electricity generation in the EU. Table 15 - Cumulative CO2 savings 2014-2025. Scenario MEPS 2014 MEPS 2019 TOTAL CO2 Savings 12,5 Mton 9,3 Mton 21,8 Mton Table 16 – CO2 Emissions and CO2 Savings (Mton) due to the transformers purchased in the period 2014-2025. CO2 (Mton) 2014 2015 2016 2017 2018 2019 2020 2021 2022 2023 2024 2025 BAU 30.586 30.103 30.113 30.122 30.395 30.354 30.148 29.599 29.600 29.602 28.422 28.404 Old Stock 30.586 28.645 27.212 25.794 24.606 23.169 21.608 19.855 18.511 17.186 15.244 13.996 1.160 2.306 3.439 4.598 5.704 5.563 5.360 5.259 5.158 4.855 4.753 1.068 2.083 3.104 4.111 4.901 5.836 1.909 2.301 2.725 3.146 3.422 3.819 1StMEPS 2ndMEPS Annual Savings - 299 595 889 1.191 1.481 5.5 Technology, functionality and innovation New technologies and improved processes in the production of transformers could significantly reduce the power losses and the associated CO2 emissions in the electricity sector. The transformer industry is a mature sector with consolidated manufacturers, and most improvements have been made gradually (e.g. improved insulation materials, lower loss magnetic steel, optimized electromagnetic design, increased amount of conductor materials) A relatively new technology which is widely used in Japan and in a smaller scale in North America uses amorphous magnetic cores. Using amorphous metal core, the no-load losses can be reduced by an additional 70 % compared to the best silicon steel. The initial purchase price of the amorphous metal based transformer is still higher than the initial price of conventional magnetic materials transformer, but the prices are coming down (see Figure 7). Comparing the use of conventional silicon steel core transformers to the use of amorphous metal based transformers, an overall financial savings during the life span of the transformer may be achieved if amorphous metal supply becomes readily available (e.g. multiple suppliers) with cost-competitive prices ( Opetuk, Zolo, & Dukic, 2010). 44 5.6 Health and safety There are no significant changes if more efficient transformers are produced, since the manufacturing process is the same. No impacts of the considered sub-options on health or safety have been identified during the preparatory study or the impact assessment. 5.7 Uncertainties and Sensitivity Analysis The robustness of the outcomes of this impact assessment study depends on the underlying assumptions. A sensitivity analysis, covering some of the most relevant factors (such as the price of energy and annual load factor) is carried out and discussed for each base case scenario. It is considered that electricity prices already incorporate external environmental costs. The analysis includes: The annual load factors that has a direct influence on the environmental impacts and LLCC of the base-cases; The electricity tariff which have an influence on the LLCC when implementing the Ecodesign measures. 5.7.1 Assumptions related to the load factors As stated in the preparatory study, average load factors were defined for each type of transformer. However, some factors can be lower or higher (see Table 17), as mentioned in the preparatory study or by stakeholders. Therefore, a sensitivity analysis is carried out for each base case to see the impact of the load factor on the electricity consumption. Table 17 – Annual Load factors used in this study. BC2 BC3 BC1 Industry Industry Distribution OIL Dry Load Factor Min Base Max 0,10 0,15 0,30 0,15 0,30 0,40 0,15 0,30 0,40 BC4 Power BC5 DER Oil BC6 DER Dry BC7 Separation/ Isolatio 0,20 0,30 0,50 0,15 0,25 0,30 0,15 0,25 0,30 0,15 0,25 0,35 45 5.7.1.1 Base Case 1 Figure 15 and Figure 16 present the results, for Base Case 1, of the sensitivity analysis on variation of the load factor. As the load factor increases, the more efficient options become more cost-effective, as the electrical losses become more significant. Figure 15 - Annual energy losses for three different cases of load factor (min, base and max)- BC1. Figure 16 -LCC for three different cases of load factor (min, base and max)- BC1 46 Therefore, it can be concluded that the LLCC for the base load factor shows little variation for a range of efficiency levels (from A0-10%Ak to A0-20%Ak-20%), but a variation in the load factors can shift up or down the efficiency values of the LLCC. 5.7.1.2 Base Case Figure 17 - Annual energy losses for three different cases of load factor (min, base and max)- BC2. Figure 18 - LCC for three different cases of load factor (min, base and max)- BC2. Therefore, it can be concluded that the LLCC for the base load factor shows little variation for a range of efficiency levels (from B0Ak-10% to A0-20%Ak-20%), but again a variation in the load factors can shift up or down the efficiency values of the LLCC. 47 5.7.1.3 Base Case 3 Figure 19 - Annual energy losses for three different cases of load factor (min, base and max)- BC3. Figure 20 - LCC for three different cases of load factor (min, base and max)- BC3. Therefore, it can be concluded that the LLCC for the base load factor is A0-20%Ak-20%. 48 5.7.1.4 Base Case 4 Figure 21 and Figure 22 present the results, for Base Case 4, of the sensitivity analysis on variation of load factor. As the load factor increases, the more efficient options become more cost-effective as the electrical losses become more significant. Figure 21-Annual energy losses for three different cases of load factor (min, base and max)- BC4. Figure 22-LCC for three different cases of load factor (min, base and max)- BC4. Therefore, it can be concluded that the LCC for the base load factor shows a significant variation for the range of different efficiency levels. With the base load factor, the LLCC level corresponds to P0-41 Pk-277. For higher load factors the load losses decrease to Pk-228, but there is no improvement in the no-load losses . 49 5.7.1.5 Base Case 5 In the Base Case 5, Figure 23 and Figure 24 show the impact of the load factor on the losses and on the LLCC. Figure 23-Annual energy losses for three different cases of load factor (min, base and max)- BC5. Figure 24-LCC for three different cases of load factor (min, base and max)- BC5. Therefore, it can be concluded that the LLCC for the base load factor is A0-20%Ak-20%. The LLCC shows little variation for a range of efficiency levels (from A0-10%Ak-20% to A020%Ak-20%), and the LLCC is robust with minimum and maximum values of load factors. 50 5.7.1.6 Base Case 6 With the Base Case 6, Figure 25 and Figure 26 show the impact of the load factor variation on the losses and on the LLCC. Figure 25-Annual energy losses for three different cases of load factor (min, base and max)- BC6. Figure 26-LCC for three different cases of load factor (min, base and max)- BC6. Based on the above figures, it can be concluded that the LLCC for the base load factor is A0-20%Ak-20%. The LLCC shows little variation with minimum and maximum values of load factors. 51 5.7.1.7 Base Case 7 In the Base Case 7, Figure 27 Figure 27 and Figure 28 show the impact of the load factor on the losses and on the LLCC. Figure 27 - Annual energy losses for three different cases of load factor (min, base and max)- BC7. 52 Figure 28 - LCC for three different cases of load factor (min, base and max)- BC7 Therefore, it can be concluded that the LLCC for the base load factor (P0-60W Pk-750W) shows a strong variation with the load factors, but the lowest value for the non-load losses (P060W) is robust in all cases. For larger load factors the designs with lower load losses (Pk in the range 500-600 W), may be cost-effective. 5.7.2 Assumptions related to the electricity tariff For the distribution transformers (excluding distributed generation DER), an average EU27 electricity tariff of 0,0935 €/kWh was used, based on the data from Eurostat. For sensitivity analysis, a plus or minus 50% variation was considered around the base price. If the lowest electricity tariff (i.e. 0,0468 €/kWh (0,5*0,0935 €/kWh)) and the highest electricity tariff (i.e. 0,1403 €/kWh (1,5*0,0935 €/kWh)) are applied, this could lead to different LLCC for the basecases load factor. The same reasoning is applicable for DER transformers (base-cases 5 and 6) when an electricity tariff of 0,1500 or 0,2250 €/kWh is used (see Table 18). Table 18- Assumptions related to electricity tariff. BC1 Distribution BC2 BC3 Industry Industry OIL Dry BC4 Power BC5 BC6 BC7 DER DER Separation/ Oil Dry Isolation 53 Electricity Min 0,0468€ 0,035 0,0750 € 0,0468€ rate Base 0,0935€ 0,05€ 0,1500 € 0,0935€ (€/kWh) Max 0,1403€ 0,075€ 0,2250 € 0,1403€ 5.7.2.1 Base Case 1 and Base Case 2 In the Base Case 1 and 2 as electricity rate increases, more efficient transformers become more economical, reducing their LCC in relation to less efficient models, as shown Figure 29 and Figure 30. Figure 29 - LCC for three different cases of electricity price (min, base and max)- BC1 54 Figure 30 - LCC for three different cases of electricity price (min, base and max)- BC2. In the near future, the trend is for electricity to become more expensive (as shown in Figure 5), so it seems very important to progressively increase the transformers efficiency . In these conditions the A0-20%Ak-20% efficiency level seems the most advantageous in the medium-long term. 5.7.2.2 Base Case 3 As in previous cases, the price of energy contributes significantly to the LCC variation, as shown in Figure 31. 55 Figure 31 - LCC for three different cases of electricity price (min, base and max)- BC3. The A0-20%Ak-20% efficiency level is the LLCC for the base electricity price. Because of the trend is for electricity to become more expensive the choice of that value becomes even more pertinent. 56 5.7.2.3 Base Case 4 As in previous cases, the price of energy contributes to the LCC variation, as shown in Figure 32. However, it can be concluded that there are minor changes in the LLCC for the different electricity prices. Figure 32-LCC for three different cases of electricity price (min, base and max)- BC4. The LLCC for the base load factor and electricity price is P0-41,Pk-277. In the near future, the trend is for electricity to become more expensive. The reduction of the transformer no-load losses does not seem to be cost-effective, even with high electricity prices, whereas the reduction of the transformer load losses to Pk-228 may become cost effective, with high electricity prices. 5.7.2.4 Base Case 5 and Base Case 6 In the Base Cases 5 and 6, the LCC as a function of the electricity rates is shown in Figures 33 and 34. 57 Life Cycle Cost for different Energy Prices-BC5 300000 250000 EUROS 200000 150000 100000 50000 0 Ck Ak Ak-10% Ak-15% Ak-20% Figure 33-LCC for three different cases of electricity price (min, base and max)- BC5. Figure 34-LCC for three different cases of electricity price (min, base and max)- BC6. The LLCC value for BC5 and BC6 for the base load factor and electricity price at the level of A0-20% Ak-20% is robust and shows little variation, becoming even more justifiable with higher electricity prices. 58 5.7.2.5 Base Case 7 As in previous cases, the price of energy contributes strongly to the LCC variation, as shown in Figure 35. Figure 35 - LCC for three different cases of electricity price (min, base and max)- BC7. Therefore, it can be concluded that the LLCC for the base electricity prices P0-60,Pk-750 shows small variation for the different efficiency levels. The reduction of the transformer noload losses is robust and cost-effective in all cases, whereas the reduction of the transformer load losses to Pk-500-600 may become marginally cost effective, with high electricity prices. 5.8 Pole mounted transformers Pole mounted transformers are less reliable and sensitive to damage, and also to theft. Thus, they are being increasingly replaced by transformers mounted on the ground in safe compartments. Since the market for small pole mounted transformers is decreasing, as overhead lines are becoming less popular compared to underground cables, the potential impact of potential regulatory measures becomes less important. The reason mentioned to keep these transformers unregulated is based on the fact that pole mounted transformers need to be light to be fitted in a pole construction, when the need for replacement comes. However, if the choice is still to replace the transformer on a pole, it should be replaced by an efficient one. Obviously, pole mounted transformers can technically also achieve class A0Ak, which is the proposed in MEPS 2014. Nevertheless, weight might be a 59 problem to mount them on some poles as currently specified by some stakeholders. Aluminum windings may be an option to decrease weight and to make theft less attractive. Heavier weight means that the specifications for sturdier poles and installers (cranes and transport) need to be modified, which can take some time to implement in tender specifications. The time horizon of 2014 seems appropriate for this purpose. Therefore the reinforcement of a pole and related costs should not be an argument to waste energy during the transformer lifetime. In summary, discarding the creation of a subcategory for pole mounted transformers avoids the risk for creating loopholes for future regulation. 60 6. Conclusions 6.1 Proposed Efficiency Levels Based and Sensitivity Analysis Results The simulation of more than 1000 design options of the different types of transformers using the simplified LCC analysis has shown that for distribution transformers, the Tier 1 level (2014) at A0Ak is a progressive intermediate stage, while Tier 2 level (2019) can be more ambitious to reach the LLCC point around A0-20%Ak-20%. For power transformers, using the base case load factor and electricity prices, the LLCC is quite similar to BAU. The customers of power transformers will many times (e.g. applications with high load factor) order better transformers than BAU, based on total cost of ownership. For small transformers the scope for improvement , as well as the savings potential, seems more limited. Therefore the MEPS at 2014 are set at BAU levels, with the 2019 MEPS showing a significant improvement for the no-load losses. The improved transformers can be achieved by the manufacturers using existing technology (e.g. high grade commercially available silicon electrical steel) and their existing manufacturing equipment. Table 19 shows the proposed MEPS levels for 2014 and 2019. Table 19- Losses levels corresponding to the four different scenarios (BAU, LLCC, BAT, Intermediate /MEPS 2014 and MESP 2019) and cumulative impacts and savings 2014-2025. Business As Usual 2014-2025 from 1 January 2014 - 2025 P0Pk Total Energy (TWh) P0Pk Energy Savings (TWh) BC1 D0Ck 206,44 A0Ak 14,79 BC2 E0Ck 143,70 A0Ak 16,59 BC3 C0Bk 47,49 A0Ak 2,99 BC4 41-326 515,03 41-294 6,00 BC5 E0Ck 4,76 A0Ak 1,84 BC6 C0Bk 20,12 A0Ak 4,77 BC7 110-750 20,72 110750 0,00 958,26 Total 46,98 Total from 1 January 2019 - 2025 P0Pk Total 2014 - 2025 Energy Savings (TWh) Energy Savings (TWh) A0-20%Ak20% A0-20%Ak20% A0-20%Ak20% 9,58 24,37 10,56 27,15 2,55 5,54 41-261 6,00 12,00 1,82 3,66 5,88 10,65 65-750 1,06 1,06 Total 37,45 84,43 A0-20%Ak20% A0-20%Ak20% 61 6.2 General Conclusions Following the principle of proportionality in the analysis, policy options 1 to 3 (Option 1: No EU Action; Option 2: Self-regulation; Option 3: Energy Labelling Only) were discarded at an earlier phase of the analysis. Regarding the Option 4 (Ecodesign MEPS Regulation on Transformers) three sub-options were analysed: -Sub-optionA - Least life cycle cost (LLCC); -Sub-option B - Best Available Technology (BAT); -Sub-option C - Intermediate 2014 first stage MEPS and 2019 second stage MEPS for the intensity of an Ecodesign regulation on transformers. The analysis carried out shows that in general, sub-option C (Intermediate 2014 first stage MEPS and 2019 second stage MEPS) optimally fulfills the objectives as set out in Section 3Objectives. The above mentioned regulation has several positive impacts, in particular the following: cost-effective reduction of transformer electricity losses; cumulative reduction of the electricity consumption of about 85 TWh, corresponding to savings of 22 Mton of CO2 by 2025 compared to the “no action” option; although there is an increased purchase cost, it will be largely compensated by savings during the use-phase of the product; reduction of the costs by economies of scale for cost-effective technologies, correction of market failures and proper functioning of the internal market; no significant administrative burdens for manufacturers or retailers; the specific mandate of the Legislator is respected; a clear legal framework for product design which leaves flexibility for manufacturers to achieve the energy efficiency levels of the 2nd stage either in two steps, or earlier (before the 2nd stage comes into effect); fair competition by creation of a level playing field; no negative impact on employment; no identified negative impact on trade. 62 Another option with similar and/or complementary impacts of sub-option C (Intermediate 2014 first stage MEPS and 2019 second stage MEPS) is to set a minimum energy efficiency requirements accompanied by a labelling scheme. A labelling system that indicates the efficiency of transformers under specific load profiles would cause a significant movement in the market promoting a healthy competition among manufacturers. The main benefits of simultaneous introduction of minimum efficiency performance standards and energy labelling requirements are the following: removal of the least efficient models from the market is guaranteed; labelling scheme is adapted to the levels of the ecodesign measure ensuring the label's long-term function as a market tool to drive up the transformers efficiency; synergistic impact of the pushing effect of the eco-design specific requirements and the pulling effect of a functioning labelling scale; complies with the demand of stakeholders for a harmonisation and rationalisation of both measures. 63 7. Monitoring and Evaluation The main monitoring element will be the tests carried out for new product conformity. Products placed on the Community market have to comply with the requirements set by the proposed regulation, as expressed by the CE marking. Monitoring of the impacts is mainly done by market surveillance carried out by Member State authorities ensuring that the requirements are met. The appropriateness of scope, definitions and concepts will be monitored by the ongoing dialogue with stakeholders and Member States. Input is also expected from work carried out in the context of upcoming Ecodesign activities on further product categories, and related activities. The main issues for a possible revision of the proposed regulation are: The appropriateness of the levels for the specific Ecodesign requirements; The appropriateness of the product scope; The possibility to enhance other environmental impacts than energy in the use phase. Taking into account the time necessary for collecting, analysing and complementing the data and experiences in order to properly assess the technological progress, a review can be presented to the Consultation Forum no later than six years after entry into force of the regulation (as required by Annex VII.9 of the Ecodesign Directive and laid down in the implementing measure). 64 8. References Opetuk, T., Zolo, I., & Dukic, G. (2010). Greening elements in the distribution networks. Journal of Industrial Engineering and Management. AEA Technology. (2011). Impact Assessment study for Sustainable Product Measures Refrigerating and freezing equipment,Transformers, Sound and imaging equipment. European Commission – DG Enterprise and Industry. Azuma, D., & Hasegawa, R. (2008). Audible Noise From Amorphous Metal and Silicon SteelBased Transformer Core. VOL. 44, NO. 11. DoE. (2011). PRELIMINARY TECHNICAL SUPPORT DOCUMENT (TSD): ENERGY EFFICIENCY PROGRAM FOR COMMERCIAL AND INDUSTRIAL EQUIPMENT:DISTRIBUTION TRANSFORMERS. Washington, DC: U.S. Department of Energy. EURELECTRIC. (2010). Power Statistics – 2010 Edition – Synopsis. Brussels. Olivares-Galva, J., de Leo, F., Georgilakis, P., & Escarela-Pérez, R. (2009). Selection of copper against aluminium windings for distribution transformers. IET Electric Power Applications. Pryor, L., Schlobohm, R., & Brownell, B. (s.d.). A COMPARISON OF ALUMINUM VS. COPPER AS USED IN ELECTRICAL EQUIPMENT. GE Consumer & Industrial. SEEDT. (2007). Strategies for development and diffusion of Energy Efficient Distribution Transformers. EU-program “Intelligent Energy Europe". SEEDT. (2008). Selecting Energy Efficient Distribution Transformers A Guide for Achieving LeastCost Solutions. Intelligent Energy Europe programme (Project no. EIE/05/056/SI2.419632). SEEDT. (2008). Strategies for development and diffusion of DistributionTransformers. EU-program “Intelligent Energy Europe". Energy Efficient SEEEDT. (2008). Strategies for development and diffusion of DistributionTransformers. EU-program “Intelligent Energy Europe". Energy Efficient UNEP & International Copper Association Southest Asia Ltd. (2011). Technical Study Report Energy Efficient Transformers. SEAN-CC. VITO & BIOIS. (2011). LOT 2: Distribution and power transformers. European Commission DG ENTR unit B1. Wuppertal Institute for Climate, Environment, Energy and SEEDT Partners. (2008). Policies and Measures Fostering Energy-Efficient Distribution Transformers. Intelligent Energy Europe programme (Project no. EIE/05/056/SI2.419632). 65 List of Annexes ANNEX 1: Minutes of Consultation Forum meeting ...........Error! Bookmark not defined. ANNEX 2: Commission Staff Working Document ...............Error! Bookmark not defined. ANNEX 3: Structure of the methodology used for establishing the technical, environmental and economic analysis ..............................Error! Bookmark not defined. ANNEX 4: Methodology to Calculate the Life Cycle Cost (LCC)Error! defined. Bookmark not ANNEX 5: Sensitive Analysis Tables ...................................Error! Bookmark not defined. ANNEX 6: Life Cycle Cost Shaded Diagram .........................Error! Bookmark not defined. ANNEX 7: Environmental Impacts (VITO & BIOIS, 2011) .....Error! Bookmark not defined. ANNEX 8: European Distribution Transformer Loss standardsError! defined. Bookmark not ANNEX 1: Minutes of Consultation Forum meeting EUROPEAN COMMISSION DIRECTORATE-GENERAL FOR ENERGY AND TRANSPORT DIRECTORATE D - New and Renewable Energy Sources, Energy Efficiency & Innovation Energy efficiency of products & Intelligent Energy – Europe Brussels, 20.04.2012 MINUTES of the Consultation Forum on small, distribution and power transformers under Article 18 of the Ecodesign of Energy-related Products Directive (2009/125/EC) on 20 April 2012 Attendees/ Presentation The list of attendees to the meeting and the Commission’s presentation are available in CIRCA as separate documents. Introductions Kirsi Ekroth-Manssila (KEM), acting Head of Unit, ENTR B.1, welcomed the Consultation Forum members and invitees to the meeting, and introduced the responsible Policy Officer for ENTR Lot 2, Cesar Santos Gil (CSG), and attending colleague, Michael Bennett (MJB). Overall Agenda – Structuring of Discussion Points CSG outlined the main purpose of the day: to inform attendees regarding the draft Ecodesign regulation for small, distribution and power transformers, and to seek feedback. Although transformers are efficient devices already, there seems to be wide consensus that an EU Ecodesign regulation establishing minimum performance requirements would be beneficial for European industry, as well for society and the environment. The details of such a proposed regulation would be presented via a structured PowerPoint presentation, based on the previously-circulated draft ENTR Lot 2 regulation working document15. CSG thanked organisations for helpful contributions received prior to the Consultation Forum, and indicated a deadline of a further 4 weeks after today's Consultation Forum for additional comments to be submitted. After an initial first round of short interventions on generic issues, the main areas of the draft document, and discussions points, would be organised according to the following structure: o o o o o 15 Scope of the proposed regulation & exceptions Definitions Ecodesign requirements for small transformers Requirements for distribution transformers Requirements for pole mounted transformers Annex 2. I o o o o o o Generic Issues Requirements for power transformers (including a discussion on Total Cost of Ownership analyses) Product information requirements Standardisation needs Verification procedure Other issues & potential loopholes AOB Comment (Anthony Walsh, Irish Electricity Board/ Eurelectric): Firstly, re. stakeholders invited to the Consultation Forum, the European Commission should explicitly consider inviting electricity utilities from Member States, plus Eurelectric. Secondly, have EU regulating bodies received the draft proposals on "Ecodesign ENTR Lot 2 – Transformers"? Thirdly, A. Walsh requests a period of more than four weeks to submit feedback, owing to the need for prior internal/ Member State-level discussions. Answer, CSG: (i, ii) – Utilities are not formally members of the Ecodesign Consultation Forum, but this could and should be addressed as they are stakeholders with a legitimate interest in the Ecodesign discussion on transformers. The Ecodesign Consultation membership was officially "frozen" at the status of 2007 (iii) It would be better to adhere to the four week deadline, wherever possible, in order to maintain the overall timeline for ENTR Lot 2. Specific Issues – Addressed Slide by Slide Re. Slide 7 – Proposed Exceptions to the Regulation CSG opens the floor for comments. Comment (Paul Jarman, National Grid, UK & Michel Sacotte, T&D Europe): Autotransformers are a simple means of increasing energy efficiency overall. Where they could be used, they should be used, i.e., they should not be excluded. Comment (Anthony Walsh, Irish Electricity Board/ Eurelectric): On the distribution side, autotransformers are not normally used. Therefore, might it be useful to classify transformers according to use by "utilities" and "non-utilities"? Technical point: differences between a "line voltage restorer" (which compensates for very short duration "sags" in voltage) and an "autotransformer". The numbers of line voltage transformers are very low. Comment (Angelo Baggini, University of Bergamo, Italy): (i) Autotransformers should be included in the measure; (ii) Any exclusions might be better addressed regarding one element of either power or function. Comment (Hans Paul Siderius, Netherlands): (i) Supports above Italian comment, and would prefer the scope to be determined by kVA; (ii) Regarding material efficiency and resource efficiency aspects, the text should be amended to state that these issues are II significant, but that they are dealt with by the functioning of the transformers market itself. Comment (Anibal de Almeida, University of Coimbra, Portugal): Supports (i) kVA approach; (ii) that autotransformers should not be excluded. Additionally, (iii) magnetic halogen lighting transformers should not be excluded. Regarding Slide 8 (Proposed Ecodesign Requirements) & Slide 9 (Proposed Definitions) Comment (Paul Jarman, National Grid, UK): The use that a transformer is put to dramatically affects its power during its lifetime, re. "load", and "on/off" usage. Therefore, denoting definitions via "rating" vs. "type of use" might be problematic. Regarding standards bodies, definitions via "rating" only would be preferred. Comment (both representatives from T&D Europe): (i) For transformers in the range 1kVA to 20 kVA, it is relatively easy to define losses. The current relevant EN & ISO standards should be taken into consideration. (ii) For "large power transformers", these are more specialised machines; T&D Europe suggests mapping their use and place in the market. (iii) Re. recyclability, most transformers are close to 95% or even 100% recyclability, and they are indeed recycled. (iv) 16.5 Hz transformers should be considered (point raised by Sweden) - however, there is the need for a study regarding their volume and total impact. Comment (Marie Baton (CLASP), & Simonetta Fumagalli (ENEA, Italy)): Care needs to be exercised to avoid double-regulation with other applicable regulations, including Ecodesign (e.g., lighting transformers, and lamp control gear). Summary (CSG): The overview conclusions seem to be to (i) exclude transformers of power <1kVA; (ii) Keep the list of function-driven exemptions as short as possible; (iii) Transformers are viewed as not being difficult to recycle - further comment on this would be appreciated from the Schneider Electric colleagues, in writing, from their experience. Regarding Slide 8, and Energy Labelling Comment (Hans Paul Siderius, NL, Stamatis Sivitos, ECOS & Roman Targosz): All express the opinion that business-to-business labelling could be useful, to indicate Best Available Technologies (BAT), with regard to resource efficiency and recyclability as well as energy performance. Comment (Michael Scholand, CLASP): Labelling is probably not appropriate re. utilities transformers, but is useful for "supply side", e.g., supply to buildings, at customer level. Industry does perform labelling, in the form of "AO, BO, AK", etc, and suggests that for ENTR Lot 2 the consideration for this Consultation Forum is whether a definition of "better than AO" could be feasible. Comment (T&D Europe, & Ireland): For the larger transformer products, market aspects already ensure recycling. An investigation to examine where a useful "borderline" might III be drawn could be useful, re. the larger transformers being recycled, vs. smaller transformers not being so successfully recycled. Regarding Slide 9 (Proposed Definitions) Comment (T&D Europe): Re. pole mounted transformers, the power rating should be 50315 kVA, because 50kVA is used in France for such transformers. Comment (University of Bergamo, Italy): Additional size grouping definitions could be usefully added, e.g., "medium power transformer", and "large/ very large power transformer". This comment was opposed by the National Grid (UK), on the grounds that all definitions should be aligned with standards. Comment (Netherlands): The European Commission should explicitly include to all relevant definitions in the Working Document, to assist consistency-checking. Comment (ENEA, Italy?): Three groups could be considered: <36kVA, >36kVA and "very high" (e.g., 1200kVA, etc). CSG, Summary: There seem to be two classes of transformers: "Distribution", and "Large Power". Regarding the 36kVA boundary issue, CSG asks Sweden to submit comments in writing. Regarding Slide 10 (Table with Proposed Ecodesign Requirements - Small Power Transformers) Comment (NL & University of Bergamo): Owing to non-linearity, from 64kVA upwards, interpolation instead of extrapolation should be required. Comment (T&D Europe): Suggest adding 80 kVA and 100 kVA extra categories to the table. Re. timeline, 2016 generally acceptable, but Tier 2 should be 2022, with respect to the changes needed to implement these requirements. CSG, Summary – Small Power Transformers: (i) The table will be extended to cover the suggested two additional categories for 80kVA and 100kVA rating. (ii) DG ENTR would appreciate contributions from stakeholders re. "rounding up" of figures. (iii) Interpolation will be required, where necessary, rather than extrapolation. Regarding Slide 11 (Table with Proposed Ecodesign Requirements – Distribution Transformers) Comment (Anthony Walsh, Irish Electricity Board/ Eurelectric): The "Total Cost of Ownership" model should be used, as kWh losses are proportional to the prices of the electricity in each Member State. If higher investment is necessary for transformers, other elements (e.g., circuits) may receive less investment. Loading patterns may change according to both transformer types, and an increased renewables component. In addition, the Tier 2 draft extra performance requirement of "-20%" in reality means that a specific type of technology is being specified, and that technology is presently largely available only outside the EU. IV Re. loading put on transformers, if, in certain areas, there is a high load, then utilities would install a second transformer to cope with this higher load. The revised scenario would mean that the average load per individual transformer would be lower over its life. Comment (Sweden): The ambition should be set higher, namely that the present "Stage 2" should become "Stage 1". For stage 2 in 2018, SE is proposing losses of Ao(-40%) for all categories in Table 2. Comment (Hitachi EU): The values in the table can be achieved with technologies available today. The timing therefore seems to be too slow, echoing Sweden's comment. AOBk is needed, because the EU is lagging behind other regions, internationally, and the timelines proposed should be strict, because of the inevitable additional time (over 2 years) for implementation to take place, for each Tier of ambition. Comment (T&D Europe): (i) Disagrees with the above two comments, and asks that the draft 2014/2018 timetable be changed to 2014 (Tier 1)/ 2020 (Tier 2). (ii) Re. losses, Member State-specific frequencies should be taken into account. (iii) The Load factor rather than "load losses" is more relevant. (iv) AOBk implies that the mass of the transformers is increased, meaning more resources are required and so the price of the transformer is likely to increase – how does this affect the overall life cycle impacts, re. embedded energy in the additional metals? Comment (CLASP Europe): Would like AOAk to be in Tier 1. Asks why Stage 2 does not demand energy improvement regarding winding losses. CLASP contends that what the Irish Electricity Board is asking for, via an approach to regulation less based on Minimum Energy Performance Standards, is no better than the status quo, and may in fact be worse than the status quo. Comment (University of Bergamo): The "Total Cost of Ownership" (TCO) approach is not mutually exclusive to the approach defining maximum losses. Legislation could define level(s) of minimum losses. Then, a "TCO" approach could be applied by utilities above these minima. Comment (Sweden): (i) Ecodesign measures must put environmental and energy requirements on products. (ii) Future-thinking is important, because new transformers will be used in the grid typically for 40 years. Question (Belgium Ministry): The TCO approach is useful, but there will be potentially always missing information. Therefore, all variables need to be included in any "TCO" approach. How may this be handled? Also, what about market surveillance and legal measures? Summary, CSG: (i) The economic figures from the preparatory study will be further explored during the Impact Assessment phase now being commenced, for large power transformers as well as distribution transformers. (ii) The ecodesign aim is that proprietary technology should not be stipulated. (iii) Comments from other utilities, in V addition to those from the Irish Electricity Board, are sought, to attempt to get a wider view from EU utilities. (iv) It should be remembered that we are discussing product policy here. The Ecodesign process is not designed to mandate public or private utilities how to conduct their procurement process; therefore, it is important to identify and specify permitted maximum losses to manufacturers, where possible. (v) It seems that not all of the conclusions from the contractor of the preparatory study (VITO) are correct, re. the Bk/ Ck discussions. (vi) The level of ambition of a recently proposed US rulemaking at present is in the region of "AOCk", allowing for frequency variations and other differential parameters, etc. (vii) For Stage 1, from the discussions it seems that there is no consensus. However, for Stage 2, there appears to be consensus on "(Ao -20%)Bk". Comment (NL & CLASP): Disagree with point (vii) above. This consensual conclusion is premature, and not ambitious enough. Answer, CSG & KEM: (i) The aim is to define maxima and minima re. EU-wide parameters. (ii) NL and CLASP comments are carefully noted. (iii) There are four more weeks in which to submit comments, so nothing is finalised. (iv) The Impact Assessment is another stage where all the facts and submissions, plus additional enquiries, will be taken into account/ initiated. LUNCH BREAK. Regarding Slide 12 – Proposed Requirements for Pole-Mounted Transformers CSG introduced Slide 12 with the overview question: Do we need a pole-mounted category? Is it a necessary sub-category? Comment (T&D Europe): Option 2 is preferred; Option 1 has too many detailed specifications. T&D will send comments in writing re. changes sought for Option 2 contents: amongst them is a request for a delay for Stage 2 from 2018 to 2020 (there are important numbers of these devices in France, and more time is needed for adaptation). Comment (Anthony Walsh, Irish Electricity Board/ Eurelectric): Option 2 is to be favoured. There are mass issues re. Option 1 in Ireland. Notes that 1.2 million poles are present in Ireland, of which 10% have transformers on them. Emphasises that Ireland will still very much need pole-mounted transformers after 2018. Comment (T&D Europe): Invites Ireland to participate in the relevant CENELEC TC 14 Working Group, re. masses of pole mounted transformers. Comment (NL): Also favours Option 2, on the grounds of being as technology-neutral as possible. Comment (CLASP, Polish Copper Promotion Centre, University of Bergamo): CLASP can accept either Option 1 or Option 2, but comments that Option 2 losses should be VI stricter, as the requirements date from 1993. CLASP favours the Stage 2 phase-out of the subcategory for pole-mounted transformers. Polish CPC also backs stricter measures, citing stricter industry proposals from 5 years previously. University of Bergamo: the values in the table are now out of scope in the EU since April 2012, apart from the worst classes . Comment (Sweden): favours combining Table 2 (Slide 11) with Table 3, Option 2 (Slide 12). Comment (Hitachi, & Anthony Walsh, Ireland): Both seek clarification re. single-phase and three-phase pole mounted transformers. CSG – clarification: ALL the values in Tab le 3 (Slide 12) refer to three-phase transformers. Comment (CLASP): Notes that the US Dept of Energy opted for an "LLCC" approach, and did not make a separate pole-mounted category for transformers. This should be examined within the Impact Assessment study for ENTR Lot 2. Comment (Anthony Walsh, Ireland): Contends that the (current/ voltage?) load is not the same in Ireland as it is in the USA; there are different wind speeds in Ireland, and different loading on power/ cables. CSG – Summary re. Pole-Mounted Transformers/ Distribution Transformers Ambition to be stepped up, as noted by stakeholders. For single-phase transformers, a separate table may be needed. Table 2 and Table 3 to be integrated; phasing out of pole-mounted category to be examined during the IA. Regarding Slides 13 & 14, and Slides 15-19 – Power Transformers Comment (T&D Europe): A Position Paper has been sent to the Commission re. a "TOC" approach (Total Cost of Ownership). In 3-4 months, T&D Europe hopes to compile a "map" of utilities' behaviour and the real market situation of power transformers. T&D Europe notes that the price of (electricity) energy varies considerably throughout the EU, and may be more volatile in some MSs (citing a smaller amount of volatility in FR, compared to IT & DE). Nordic countries have a "TOC" approach which is more heavily-weighted towards energy costs. Manufacturers are very willing to promote energy saving in the EU via stricter standards, especially if this also ensures that jobs and technology development are maintained in the EU. Comment (UK): Option 2 is better, regarding minimum efficiency, based on TCO. This should be agreed with CENELEC. Prefers TCO plus a minimum energy efficiency standard. VII Comment (SWE): Favours either Option 1 or 2. A solution that Sweden would support is to set a price per kWh lost. This is set politically, in Sweden. This could be an interim solution re. Ecodesign requirements. Comment (Hitachi): Supports minimum efficiency measures. This could also be extended to distribution transformers. Comment (Polish CPC): Favours Option 2. However, does not agree with combining/ discussing together power transformers and distribution transformers., as a consensus on using maximum losses for distribution transformers is very close. Comment (University of Bergamo): Medium-sized transformers are more homogeneous. Large transformers are more heterogeneous. Thus, owing to this lack of mass-scale homogeneity, an approach similar to the Energy Performance of Buildings Directive might be useful, i.e., assess each site on its own merits. Comment (CLASP): Supports Option 2. Re. the role of CENELEC, comments that CENELEC's role should be re. the equation and method for energy efficiency, but not the level of efficiency stipulated in the ecodesign regulation. CLASP supports the setting up of a Technical Committee/ Working Group, because in its opinion, much of the information sought is actually available within organisations – it just needs to be discussed meaningfully by relevant practitioners. Comment (Oekopol): Supports Option 2, but timing must not be delayed. Rejects Option 3. Comment (UK): Recommends examining the CENELEC and IEC available equations. Also recommends extending the provisions for large transformers to those which are <36kV, where loading makes this suitable/ necessary. Comment (Anthony Walsh, Irish Electricity Board/ Eurelectric): Notes the absence of distribution/ transmission stakeholders during today's discussions, and comments that some design parameters of the electricity networks could have important ramifications for transmission stakeholders. Another point is whether, and to what amount, the effects of a higher proportion of renewables in the grid might have to be evaluated, re. when excess electricity is available. Summary – CSG: Cites the US use of load and non-load losses combined in a single formula for energy efficiency, so it must be possible to do it. Option 2 – to try, for large power transformers. Aiming for Autumn 2012 solution availability. Expert Group – to be convened, with limited numbers, and expert participants. VIII Regarding Slides 20-22 – Product Information Requirements, Standardisation Needs, Verification Procedure (Annex IV) Comment (Sweden, UK): Mineral oils in transformers, plus other fluids and gases. Need to be addressed, re. fire precautions also, and care must be exercised not to make technology-specific requirements in Ecodesign measures. UK: Care also is needed re. definitions on declared losses, as opposed to measured losses or design losses.. Comment (DE, AT): Re. market surveillance, there might be more of an issue re. "putting into service", rather than "placing on the market". Summary, CSG: Notes that Special Small Powered Transformers are out of scope for specific ecodesign requirements, but are in scope re. product information requirements. This will be clarified in the draft regulation. Notes that the "caution mark" is addressed to market surveillance authorities, as this is a subcategory product with different provisions in the regulation. Asks for clarification from stakeholders re. "plates" where losses are indicated, vis-à-vis measured losses, and associated liabilities. Comment (T&D Europe): "Declared value" should instead be termed "Guaranteed value". Comment (NL): Re. B2B deals, "guaranteed value" is the term to be preferred, generally. However, in ecodesign, the terminology would be "declared value", for one individual transformer, rather than (e.g., in B2B contracts) the average performance over a batch. Comment (University of Bergamo): The parameter rated power should be included as a measured parameter in the verification procedure in order to avoid false declarations. A value of 5% is considered reasonable as a tolerance for all measured parameters. Summary – CSG: The phrase "on the nameplate" will be added to the sentence, re. Slide 22 specifications. Rated power will be included as a parameter and tolerances of 5% will be specified. Comment (Anthony Walsh, Ireland): Retrofitting – should be looked at, re. existing size constraints in, e.g., the nacelle of a wind turbine, or an existing substation. Comment (NL): Strong disagreement with the position of A.Walsh. Such potential exemptions could create loopholes, which would render the whole Ecodesign process meaningless for transformers. Such exemptions re. retrofitting taking into account sitespecific requirements etc, should only be allowed re. historic, listed buildings. See, for example, the recent Air-conditioning Ecodesign Regulation, which did this. Comment (Polish CPC): As the rate of refurbishment of transformers is low, especially where transformers are aged over 20 years, a refurbishment maximum of 10 years could be considered. IX Comment (UK, ?or UK National Grid?): Notes that the time period between specification and construction for bespoke transformers can be over 1 year. Therefore, UK requests a period of "stability" of 3-5 years, re. regulations in which specifications can be made, re. losses and production requirements. Second point (UK, and Polish CPC): "rated power" for larger transformers – care re. definitions are needed. In the UK, there is a "base rating", and an "emergency rating". This could be important in other MSs. "Emergency rating" is important re. over-loading, in certain instances, as required. Comment (Oekopol): Public procurement – GPP should link up with Ecodesign requirements, to ensure a coherent approach. Summary – CSG: (i) Asks for responses by 18 May (ii) Reminds stakeholders that he will contact stakeholders re. their interest for participating in the Technical Group. (iii) Next Ecodesign Consultation Forum will be held in Autumn 2012, which will hopefully be able to take into account the recommendations of the Technical Group (point ii) by that time. 17.00: Close of meeting. X ANNEX 2: Commission Staff Working Document Working document on a Commission Regulation implementing Directive 2009/125/EC with regard to small, medium and large power transformers 18/10/2012 Brussels THE EUROPEAN COMMISSION, Having regard to the Treaty on the Functioning of the European Union, Having regard to Directive 2009/125/EC of the European Parliament and of the Council of 21 October 2009 establishing a framework for the setting of ecodesign requirements for energy-related products ( 1 ) and in particular Article 15(1) thereof, After consulting the Ecodesign Consultation Forum, Whereas: (1) The Commission has carried out a preparatory study which analysed the environmental and economic aspects of transformers. The study has been developed together with stakeholders and interested parties from the Community and the results have been have made publicly available. (2) The study showed that energy in the use phase is the most significant environmental aspect which can be addressed through product design. Significant amounts of raw materials (copper, iron) are used in the manufacturing of transformers, but market mechanisms seem to be ensuring an adequate end-of-life treatment, and therefore, for the time being, related mandatory ecodesign requirements are not being set out. (3) Mandatory ecodesign requirements apply to products placed on the market or put into service wherever they are installed, therefore such requirements cannot be made dependant on the application in which the product is used. (4) Ecodesign requirements for the energy performance of medium power transformers and for the energy efficiency of large power transformers should be set with a view to harmonising ecodesign requirements for these devices throughout the Community and contributing to the functioning of the internal market and to the improvement of their environmental performance. (5) This Regulation should increase the market penetration of technologies and design options improving the energy performance of medium power transformers and the energy efficiency of large power transformers. The cost-effective improvement potential through design is about XX TWh per year in 2020, which corresponds to XX Mt of C02 emissions (to be completed once requirements are stable). XI (6) A staged entry into force of the ecodesign requirements should provide an appropriate timeframe for manufacturers to redesign their products. The timing of the stages should be set in such a way that cost impacts for manufacturers, in particular SMEs, are taken into account, while ensuring timely achievement of the policy objectives. (7) In the procurement of medium and large power transformers, most end-users (including public and private utilities and industrial site owners) perform loss capitalisation calculations in order to determine the financially optimal levels of energy losses. Wide variations in the estimates for wholesale electricity prices and capital discount rates make it difficult for economic operators to compare design options across Member States. End-users and manufacturers are therefore advised to use reliable sources for the estimates of wholesale electricity prices, such as the Statistics and Market observatory provided by the European Commission16. (8) In order to facilitate compliance checks, manufacturers should be requested to provide information in the technical documentation referred to in Annexes IV and V to Directive 2009/125/EC. Subject matter and scope This working document pursuant to Directive 2009/125/EC establishes ecodesign requirements related to small, medium and large power transformers with a minimum power rating of 1 kVA used in 50Hz electricity transmission and distribution. This Regulation shall not apply to the following categories of transformers: Instrument transformers Traction transformers on rolling stock Starting transformers Testing transformers Welding transformers Explosion-proof and underground mining transformers Transformers for deep water (submerged) applications Definitions Transformers are considered as energy related products within the meaning of Article 2 (1) of Directive 2009/125/EC. For the purpose of this working document and its annexes the following definitions shall apply. “Power transformer” means a static piece of apparatus with two or more windings which, by electromagnetic induction, transforms a system of alternating voltage and 16 http://ec.europa.eu/energy/observatory/electricity/electricity_en.htm XII current into another system of alternating voltage and current usually of different values and at the same frequency for the purpose of transmitting electrical power. “General purpose small power transformer” means a power transformer with a highest voltage for equipment not exceeding 1 kV.. “Medium power transformer” means a power transformer with a high voltage winding with a rated voltage higher than 1 kV, but not exceeding 36 kV. “Large power transformer” means a power transformer with a high voltage winding having a rated voltage exceeding 36 kV. “Liquid-immersed transformer” means a power transformer in which the magnetic circuit and windings are immersed in liquid. “Dry-type transformer” means a power transformer in which the magnetic circuit and windings are not immersed in an insulating liquid. “Pole mounted transformer” means a power transformer connected by open bushings suitable for outdoor service and designed to be mounted on the support structures of overhead power lines. (1) “Winding” refers to the assembly of turns forming an electrical circuit associated with one of the voltages assigned to the transformer. (2) Rated voltage of a winding (Um) is the voltage assigned to be applied, or developed at no-load, between the terminals of an untapped winding, or of a tapped winding connected on the principal tapping. (3) “High-voltage winding” refers to the winding having the highest rated voltage. (4) “Rated power” (S) is a conventional value of apparent power assigned to a winding which, together with the rated voltage of the winding, determines its rated current. (5) “Load factor” means the ratio of energy supplied by a transformer during a given period of time to the energy it would have supplied if it had been operating at its maximum rated power for the same period of time. (6) “Load loss” (Pk) means the active power absorbed at rated frequency and reference temperature associated with a pair of windings when the rated current (tapping current) is flowing through the line terminal(s) of one of the windings and the terminals of the other windings are in short-circuit with any winding fitted with tappings connected to its principal tapping (any other windings, if existing, are open-circuited). (7) “No load loss” (Po) means the active power absorbed at rated frequency when the transformer is energised and the secondary circuit is open. The applied voltage is the rated voltage, and if the energized winding is fitted with a tapping, it is connected to its principal tapping. Eco-design requirements Energy losses in the use phase are by far the dominating environmental impact over the lifecycle of transformers. XIII Products falling under the definitions of paragraph "Definitions" above shall meet the ecodesign requirements set out in Annex I, including: Minimum energy performance requirements for medium power transformers Peak efficiency requirements for large power transformers Product information requirements Form of the Implementing measure The Commission intends to propose a directly applicable Implementing Regulation under Directive 2009/125/EC. The proposed Regulation is not expected to have a particular impact on the EU acquis. There are no overlaps with other Ecodesign regulations, as far as is known. Conformity Assessment A conformity assessment shall be carried out according to Chapter 8 of Directive 2009/125/EC, Annex IV (Internal design control) or Annex V (Management system for assessing conformity). Verification procedure for market surveillance purposes When performing the market surveillance checks referred to in Directive 2009/125/EC, Chapter 3 (2), Member State authorities shall apply the verification procedure set out in Annex III. Benchmarks The indicative benchmarks for the best available technology currently available on the market are identified in Annex IV. Revision No later than six years after entry into force of this Regulation, the Commission shall review it in the light of technological progress and present the results of this review to the Consultation Forum. Entry into force The Regulation shall enter into force on the 20th day following its publication in the Official Journal of the European Union. The requirements set out in Annex I shall apply in accordance with the timetable provided for therein. XIV Annex I: Ecodesign requirements a) Specific requirements for general purpose small power transformers The minimum energy performance requirements for small power transformers consist of maximum allowed load and no-load losses given in Table I.1. Table I.1: Maximum load and no-load losses requirements for general purpose small power transformers Tier 1 (1 July 2014) Maximum Rating (S) (kVA) Maximum no-load load losses losses (W)* (W)* 25 100 1 55 200 4 Tier 2 (1 July 2018) Maximum noMaximum load losses (W)* load losses (W)* 21 85 45 170 16 110 400 90 340 32 165 600 135 510 64 220 800 180 680 80 285 1025 230 875 100 345 1245 280 1060 *Maximum losses for kVA ratings that fall in between the ratings in Table I.1 shall be obtained by linear interpolation. Maximum losses for kVA ratings that fall outside the ratings in Table I.1 shall be obtained by linear extrapolation. XV b) Specific requirements for medium power transformers The minimum energy performance requirements for medium power transformers consist of maximum allowed load and no-load losses given in Tables I.2 to I.7 b.1) Specific requirements for medium power transformers with rated power <4000kVA Table I.2: Maximum load and no-load losses for liquid-immersed medium power transformers with the high-voltage winding rated ≤ 24 kV and the other winding rated ≤ 1,1 kV Tier 1 (from 1 July 2014) RATED POWER (kVA) Short-circuit impedance in () Maximum load losses (in Watts) * Tier 2 (from 1 July 2018) Maximum no-load losses (in Watts)* Pole mounted Pole mounted Maximum load losses (inWatts)* Maximum no-load losses (in Watts)* (Pole mounted sub-category disappears) 25 (4%) Bk(725) Ao(70) Ao(70) Ak(600) Ao-20%(56) 50 (4%) Bk(875) Ao(90) Ao(90) Ak(750) Ao-20%(72) 100 (4%) Bk(1250) Ao(145) Ao(145) Ak(1250) Ao-20%(116) Ao(210) Ao(210) Ak(1750) Ao-20%(168) 160 (4%) Bk(2000) Ck+32%(3100)** 250 (4%) Bk(2750) Ao(300) Co(425)** Ak(2350) Ao-20%(240) 315 (4%) Bk(3250) Ao(360) Co(520)** Ak(2800) Ao-20%(288) 400 (4%) Bk(3850) Ao(430) Ak(3250) Ao-20%(344) 500 (4%) Bk(4600) Ao(510) Ak(3900) Ao-20%(408) 630 (4%) Bk(5400) Ao(600) Ak(4600) Ao-20%(480) 800 (6%) Ak(6000) Ao(650) Ak(6000) Ao-20%(520) 1000 (6%) Ak(7600) Ao(770) Ak(7600) Ao-20% (616) 1250 (6%) Ak(9500) Ao(950) Ak(9500) Ao-20%(760) 1600 (6%) Ak(12000) Ao(1200) Ak(12000) Ao-20%(960) 2000(6%) Ak(15000) Ao(1450) Ak(15000) Ao-20%(1160) 2500(6%) Ak(18500) Ao(1750) Ak(18500) Ao-20%(1400) 3150(6%) Ak(23000) Ao(2200) Ak(23000) Ao-20%(1760) *Maximum losses for kVA ratings that fall in between the ratings given in Table I.2 shall be obtained by linear interpolation. Maximum losses for kVA ratings falling outside those given in this table shall be obtained by exponential extrapolation with exponent 0,75. ** These levels of load and no load losses represent concessions made because of the weight limitations for mounting transformers on poles. In order to avoid misuse of transformers specifically manufactured for pole-mounted operation, they should include a visible display “For pole-mounted operation only”, so as to facilitate the work of national market surveillance authorities. XVI Table I.3: Maximum load and no-load losses for dry-type medium power transformers with the high-voltage winding rated ≤ 24 kV and the other winding rated ≤ 1,1kV Tier 1 (1 July 2014) Tier 2 (1 July 2018) RATED POWER (kVA) Short-circuit impedance 6% Maximum load losses (in Watts)* Maximum no-load losses (in Watts)* Maximum load losses (in Watts)* Maximum no-load losses (in Watts)* 50 Ak(1500) Ao(200) Ak(1500) Ao-20%(160) 100 Ak(1800) Ao(280) Ak(1800) Ao-20%(224) 160 Ak(2600) Ao(400) Ak(2600) Ao-20%(320) 250 Ak(3400) Ao(520) Ak(3400) Ao-20%(416) 400 Ak(4500) Ao(750) Ak(4500) Ao-20%(600) 630 Ak(7100) Ao(1100) Ak(7100) Ao-20%(880) 800 Ak(8000) Ao(1300) Ak(8000) Ao-20%(1040) 1000 Ak(9000) Ao(1550) Ak(9000) Ao-20%(1240) 1250 Ak(11000) Ao(1800) Ak(11000) Ao-20%(1440) 1600 Ak(13000) Ao(2200) Ak(13000) Ao-20%(1760) 2000 Ak(16000) Ao(2600) Ak(16000) Ao-20%(2080) 2500 Ak(19000) Ao(3100) Ak(19000) Ao-20%(2480) 3150 Ak(22000) Ao(3800) Ak(22000) Ao-20%(3040) *Maximum losses for kVA ratings that fall in between the ratings given in Table I.3 shall be obtained by linear interpolation. Maximum losses for kVA ratings falling outside those given in this table shall be obtained by exponential extrapolation with exponent 0,75. Table I.4: Maximum load and no-load losses for other combinations of winding voltages (rated power < 4000kVA) One winding with Um ≤ 24 kV and the other with Um > 1,1 kV The levels of losses indicated in Tables I.2 and I.3 can be increased by 10% for no load losses and by 10% for load losses One winding with Um = 36 kV and the other with Um ≤ 1,1 kV The levels of losses indicated in Tables I.2 and I.3 can be increased by 15% for no load losses and by 10% for load losses One winding with Um = 36 kV and the other with Um > 1,1 kV The levels of losses indicated in Tables I.2 and I.3 can be increased by 20% for no load losses and by 15% for load losses Case of dual voltage on the same winding The levels of losses indicated in Tables I.2 and I.3 can be increased by 15% for no load losses and by 10% for load losses in case of one dual voltage on one winding Case of dual voltage on both windings The levels of losses indicated in Tables I.2 and I.3 can be increased by 25% for no load losses and by 25% for load losses in case of dual voltage on both windings (the level of losses for this kind of transformer is given on higher voltage) XVII b.2) Specific requirements for medium power transformers with rated power ≥4000kVA Table I.5: Maximum load and no-load losses for liquid immersed medium power transformers with the high-voltage winding rated ≤ 24 kV and the other winding rated ≥ 1,1 kV Tier 1 (1 July 2014) Tier 2 (1 July 2018) RATED POWER (kVA) Short-circuit impedance (%) Maximum load losses (in Watts)* Maximum no-load losses (in Watts)* Maximum load losses (in Watts)* Maximum no-load losses (in Watts)* 4000 8-10 Ak(30000) Ao(2800) Ak(30000) Ao-20%(2240) 5000 8-10 Ak(33000) Ao(3300) Ak(33000) Ao-20%(2640) 6300 8-10 Ak(37000) Ao(4000) Ak(37000) Ao-20%(3200) 8000 8-10 Ak(42000) Ao(4800) Ak(42000) Ao-20%(3840) 10000 8-10 Ak(48000) Ao(5800) Ak(48000) Ao-20%(4640) 12500 9-11 Ak(55000) Ao(7000) Ak(55000) Ao-20%(5600) 16000 9-11 Ak(66000) Ao(8500) Ak(66000) Ao-20%(6800) 20000 9-11 Ak(78000) Ao(10500) Ak(78000) Ao-20%(8400) 25000 9-12 Ak(92000) Ao(13000) Ak(92000) Ao-20%(10400) 31500 9-12 Ak(112000) Ao(16000) Ak(112000) Ao-20%(12800) 36000 9-12 Ak(125000) Ao(18000) Ak(125000) Ao-20%(14400) 40000 9-12 Ak(136000) Ao(20000) Ak(136000) Ao-20%(16000) *Maximum losses for kVA ratings that fall in between the ratings given in Table I.5 shall be obtained by linear interpolation. Maximum losses for kVA ratings falling outside those given in this table shall be obtained by exponential extrapolation with exponent 0,75. Table I.6: Maximum load and no-load losses for dry type medium power transformers with the high-voltage winding rated above 1,1 kV but below 24 kV and the other winding rated ≥ 1,1kV Tier 1 (1 July 2014) Tier 2 (1 July 2018) RATED POWER (kVA) Short-circuit impedance (%) Maximum load losses (in Watts)* Maximum no-load losses (in Watts)* Maximum load losses (in Watts)* Maximum no-load losses (in Watts)* 4000 7 Ak(28000) Ao(5000) Ak(28000) Ao-20%(4000) 5000 8 Ak(35000) Ao(6000) Ak(35000) Ao-20%(4800) 6300 8 Ak(44000) Ao(7500) Ak(44000) Ao-20%(6000) 8000 8 Ak(55000) Ao(9500) Ak(55000) Ao-20%(7600) 10000 8 Ak(68000) Ao(12000) Ak(68000) Ao-20%(9600) *Maximum losses for kVA ratings that fall in between the ratings given in Table I.6 shall be obtained by linear interpolation. Maximum losses for kVA ratings falling outside those given in this table shall be obtained by exponential extrapolation with exponent 0,75. XVIII Table I.7: Maximum load and no-load losses for medium power transformers with other combinations of winding voltages (rated power > 4000kVA) One winding with Um = 36 kV and the other one with 1,1 kV < Um ≤ 24 kV The levels of losses indicated in Tables I.5 and I.6 can be increased by 15% for no load losses and by 10% for load losses Both windings with 24 kV < Um ≤ 36 kV The levels of losses indicated in Tables I.5 and I.6 can be increased by 25% for no load losses and by 15% for load losses b.3) Specific requirements for medium power transformers with other characteristics b.3.1) Load and no load losses for transformers equipped with tapping +/-5% When transformers are equipped with tap changers, the levels of load and no load losses in the relevant table of this Annex I, can be increased by 10%. XIX c) Specific requirements for large power transformers (>36kV) The minimum peak energy efficiency requirements for large power transformers are set out in Table I.8. The methodology for calculating the peak energy efficiency is available in Annex II. Table I.8 Minimum peak energy efficiency requirements for large power transformers RATED POWER (kVA) Tier 1 (1 July 2014) Tier 2 (1 July 2018) η max (%) * η max (%) * 4000 5000 10000 25000 40000 50000 80000 100000 150000 250000 350000 *Minimum peak efficiency levels for kVA ratings that fall in between the ratings given in this table shall be obtained by linear interpolation. Minimum peak efficiency levels for kVA ratings falling outside those given in this table shall be obtained by exponential extrapolation with exponent 0,75. The Technical Subgroup on Large Power Transformers will present to the Ecodesign Consultation Forum options to be considered for setting out mandatory minimum peak efficiency requirements. XX d) Product information requirements From 01.07.2014 the following product information requirements apply: (1) Information on rated power, load loss17 and no-load loss18 and the electrical power of any cooling system required at no load shall be mandatory in any related product documentation, as well as on the transformer’s rating plate. (2) For large power transformers, the peak efficiency and the power at which it occurs shall be marked on the rating plate. (3) Information on the weight of all the main components of a transformer (including the conductor, the nature of the conductor and the core material) shall be mandatory in any related product documentation. (4) Special small power purpose transformers with well defined target applications shall have their application identified in any related product documentation and shall include the ISO caution mark to read the product documentation. (5) Pole mounted distribution transformers as defined in this Regulation shall have their application mentioned in any related product documentation and shall include the ISO caution mark to read their documentation. In order to avoid misuse of transformers specifically manufactured for pole-mounted operation, they should also include a visible display “For pole-mounted operation only”, so as to facilitate the work of national market surveillance authorities. 17 17 Corrected to reference temperature XXI Annex II: Measurement methods 1. For the purpose of compliance with the requirements of this Regulation, measurements shall be made using a reliable, accurate and reproducible measurement procedure, which takes into account the generally recognised state of the art measurement methods, including methods set out in documents the reference numbers of which have been published for that purpose in the Official Journal of the European Union. A European Standard EN xxxx for “Three-phase medium voltage transformers 50Hz, with highest voltage for equipment not exceeding 36 kV” is likely to be voted by CENELEC in the next six months. This European Standard should then become a harmonized standard) in support of this Ecodesign Regulation (through the publication of its reference in the OJEU) by the time it has been adopted. 2. Calculation method for the energy efficiency η max of large power transformers. The methodology for calculating the energy efficiency of a specific transformer is based on the load and no load losses that occur at the operation point of maximum efficiency. The formula includes the apparent power at which the losses are measured. where Po is the no load losses (*) Pco is the electrical power required by the cooling system for no load operation Pk is the load losses(*) corrected to reference temperature(**) Sr is the (apparent) rated power of the transformer at which Pk is measured. (*) (**) measured at rated voltage and rated frequency, on the rated (nominal?) tap as defined in EN IEC 60076-1:2011 XXII Annex III: Verification procedure for market surveillance purposes When performing the market surveillance checks referred to in Article 3(2) of Directive 2009/125/EC, the authorities of the Member States shal apply the following verification procedure for the requierements set out in Annex I. 1. The authorities of the Member State shall test one single unit 2. The model shall be considered to comply with the povisions set out in this Regulation if the measured parameters meet the values declared by the supplier within the ranges set out in Table 1 3. If the result referred to in point 2 is not achieved: − For models that are produced in lower quantities than x per year, the model shall be considered not to comply with this Regulation − For models that are produced in quantities of x or more per year, the market surveillace authority shall randomly test x additional units 4. The model shall be considered to comply with the provisions set out in this Regulation if the averages of all the measured parameters referred to in Table 1 do not vary from the values set out in Annex I by more than 5% 5. If the results referred to in point 4 are not achieved, the model shall be considered not to comply with this Regulation. For the pruposes of checking conformity with the requierements of this Regulation, Member States authorities shall use reliable, accurate and reproducible measurement procedures, which take into account the generally recognised state-of-the-art measurement methods, including methods set out in documents the reference numbers of which have been published for that purpose in the Official Journal of the European Union. Table 1. Measured parameter Load losses No load losses Verification tolerances The measured value shall not be greater than the declared value by more than 5 %. The measured value shall not be greater than the declared value by more than 5 %. XXIII Annex IV: Indicative benchmarks At the time of adoption of this Regulation, the best available technology widely available in the EU market for the products concerned has been identified as follows: - Liquid-immersed medium power transformer: No-load losses Ao-20%, load losses Ak20% - Dry-type medium power transformer: No-load losses Ao-20%, load losses Ak-20% The Commission seeks confirmation from stakeholders as to whether the above benchmarks identified in the preparatory study and the impact assessment study are adequate. XXIV ANNEX 3: Structure of the methodology used for establishing the technical, environmental and economic analysis Following the "Methodology Study Eco-design of Energy Using Products" ("MEEuP"), the tasks listed below are carried out for developing the technical, environmental and economic analysis referred to in Annex II of the Ecodesign Directive: Task 1: Definition Task 2: Economic and market analysis Task3: User Behaviour Task 4: Assessment of Base-Case Task 5: Technical Analysis BAT and BNAT Task 6: Improvement Potential Task 7: Policy and Impact Analysis ANNEX 4: Methodology to Calculate the Life Cycle Cost (LCC) XXV The methodology followed was based on a wide range of core and coil losses for each transformer analysed, including from the highest allowable level (usually Co and Ck) to a point beyond the most efficient levels (i.e., called Ao and Ak). The combinations of core and coil losses combine to create several combinations of Po and Pk. For each combination, the kWh/year consumed is calculated, along with the Life Cycle Cost (LCC) of those losses. Then, the cost of the transformer is calculated for each design based on the equation associated with a curve‐fit of the Preparatory Study designs. Finally, with first cost and operating cost known, the respective LCC is calculated for the entire matrix of designs. The following text discusses the steps involved in more detail: 1. Establishing the Range of Losses: each of the base case transformers analysed has a range of losses that are given in the Preparatory Study. The spreadsheet starts with the least efficient design, which constitutes the baseline unit for analysis, and then extends out to lower maximum loss levels until the A0 and Ak levels are surpassed. Going beyond the A0, Ak level (A0-20% and Ak-20%) is important because it offers some insight into the economics of models slightly above the highest conventional levels considered in the Preparatory Study. 2. Calculate kWh/year consumption: given the known losses for the transformer (P0, Pk), it is known that the P0 losses will be occurring 8.760 hours per year, thus those can be deducted from the kWh/year total consumption reported in the Preparatory Study. The remaining kWh/year is then divided by Pk, and a constant is derived, which is a function of the transformer loading determined by VITO for the Preparatory Study. 3. Calculate purchase price of the transformer: each of the Preparatory Study designs is plotted on a graph showing purchase price over kWh/year of energy consumption. This metric is used for the X‐axis because it takes into account both P0 and Pk, as well as the embedded assumptions about average loading. A curve is fit to those data, using either a 2nd or 3rd order polynomial or exponential equation, which is a function of the kWh/year losses. The equation is then multiplied by the different kWh/year calculated for each P0, Pk combination to estimate a price for each of the designs. 4. Calculate LCC of operating costs: the LCC of operating the transformer can be calculated by multiplying the different kWh/year calculated for each P0, Pk combination with the energy prices and adding to this result the purchase price of transformer. 5. Calculate the LCC relative to the baseline model and provide colour coding: the LCC is then derived by summing together the purchase price and the operating LCC, resulting in a total LCC for the transformer. XXVI In order to perform these calculations for the base case models, there are certain key data points taken from the Preparatory Study that drive the whole simplified LCC model. The following key data points are given in Chapter 6 of the Preparatory Study for each base case unit and each of the more efficient designs prepared at that same kVA rating: Maximum watts of core loss (P0); Maximum watts of coil loss (Pk); Annual energy consumption from the transformer (kWh/year); Price of the transformer (Euro); Total electricity cost (Euro/year); LCC for the lifetime of the transformer. Polynomial fit-curve overlays used to estimate the purchase price of each transformer design -BC1 -BC2 XXVII -BC3 -BC4 XXVIII -BC5 XXIX -BC6 -BC7 XXX ANNEX 5: Sensitive Analysis Tables BC1 LIFE CYCLE COST D0 C0 B0 A0 A0-10% A0-15% A0-20% 4600 Ck 13606 12581 12368 12502 12689 12809 12956 Price Energy- Min (€) 3850 3250 2925 2763 Bk Ak Ak-10% Ak-15% 13370 13200 13114 13073 12490 12435 12412 12402 12369 12389 12406 12416 12597 12690 12747 12778 12828 12957 13033 13073 12970 13116 13202 13246 13139 13303 13399 13448 2600 Ak-20% 13033 12394 12427 12809 13114 13292 13499 D0 C0 B0 A0 A0-10% A0-15% A0-20% 4600 Ck 20877 18718 17775 17180 17019 16969 16937 Price Energy - Base (€) 3850 3250 2925 2763 Bk Ak Ak-10% Ak-15% 20448 20122 19952 19869 18433 18222 18115 18063 17582 17446 17379 17347 17080 17018 16991 16979 16963 16936 16929 16926 16935 16925 16927 16929 16925 16934 16946 16953 2600 Ak-20% 19786 18012 17316 16969 16925 16933 16962 D0 C0 B0 A0 A0-10% A0-15% A0-20% 4600 Ck 28149 24855 23183 21858 21348 21128 20917 Price Energy - Max (€) 3850 3250 2925 2763 Bk Ak Ak-10% Ak-15% 27525 27043 26789 26664 24375 24009 23818 23724 22795 22504 22352 22278 21564 21346 21235 21181 21098 20916 20824 20780 20899 20735 20652 20612 20712 20565 20492 20458 2600 Ak-20% 26540 23631 22205 21128 20736 20574 20424 W 750 610 520 430 387 366 344 W 750 610 520 430 387 366 344 W 750 610 520 430 387 366 344 ENERGY LOSSES D0 C0 B0 A0 A0-10% A0-15% A0-20% 4600 Ck 7143 5916 5128 4340 3963 3779 3586 Total Losses - Min (kWh) 3850 3250 2925 2763 2600 Bk Ak Ak-10% Ak-15% Ak-20% 7049 6975 6934 6914 6894 5823 5748 5708 5688 5667 5035 4960 4919 4899 4879 4246 4171 4131 4111 4091 3869 3795 3754 3734 3714 3686 3611 3570 3550 3530 3493 3418 3378 3357 3337 D0 C0 B0 A0 A0-10% A0-15% A0-20% 4600 Ck 7859 6632 5844 5056 4679 4495 4302 Total Losses - Base (kWh) 3850 3250 2925 2763 2600 Bk Ak Ak-10% Ak-15% Ak-20% 7649 7481 7389 7344 7298 6422 6254 6163 6118 6072 5634 5466 5375 5329 5284 4845 4677 4586 4541 4495 4469 4301 4210 4164 4119 4285 4117 4026 3980 3935 4092 3924 3833 3788 3742 D0 C0 B0 A0 A0-10% A0-15% A0-20% 4600 Ck 11725 10498 9710 8922 8545 8361 8168 Total Losses - Max (kWh) 3850 3250 2925 2763 2600 Bk Ak Ak-10% Ak-15% Ak-20% 10884 10212 9848 9666 9484 9658 8986 8621 8440 8257 8870 8197 7833 7651 7469 8081 7409 7045 6863 6680 7705 7032 6668 6486 6304 7521 6848 6484 6302 6120 7328 6655 6291 6110 5927 W 750 610 520 430 387 366 344 W 750 610 520 430 387 366 344 W 750 610 520 430 387 366 344 XXXI BC2 LIFE CYCLE COST E0 D0 C0 B0 A0 A0-10% A0-15% A0-20% 13000 Dk 32215 30928 29493 28782 28142 27907 27806 27714 10500 Ck 30768 29337 28130 27693 27459 27448 27466 27503 Price Energy- Min (€) 9000 7600 6840 Bk Ak Ak-10% 29805 28949 28531 28486 27869 27636 27614 27445 27508 27447 27601 27870 27570 28133 28654 27744 28514 29161 27859 28736 29449 27998 28989 29770 6460 Ak-15% 28340 27551 27586 28058 28977 29551 29872 30231 6080 Ak-20% 28163 27490 27698 28284 29343 29986 30344 30739 E0 D0 C0 B0 A0 A0-10% A0-15% A0-20% 13000 Dk 54192 50985 47631 45897 44169 43441 43097 42756 10500 Ck 50610 47260 44133 42673 41352 40847 40623 40410 Price Energy - Base (€) 9000 7600 6840 Bk Ak Ak-10% 48366 46315 45248 45128 43316 42433 42337 40972 40386 41146 40105 39724 40181 39549 39421 39862 39437 39435 39734 39416 39480 39624 39420 39552 6460 Ak-15% 44732 42024 40140 39588 39419 39500 39579 39688 6080 Ak-20% 44231 41638 39927 39490 39461 39611 39726 39872 E0 D0 C0 B0 A0 A0-10% A0-15% A0-20% 13000 Dk 76169 71043 65769 63011 60196 58975 58388 57797 10500 Ck 70452 65182 60137 57652 55244 54247 53779 53317 Price Energy - Max (€) 9000 7600 6840 Bk Ak Ak-10% 66927 63680 61965 61770 58762 57231 57059 54499 53264 54845 52608 51579 52793 50965 50188 51981 50360 49709 51610 50096 49511 51250 49850 49334 6460 Ak-15% 61125 56497 52694 51118 49861 49450 49286 49145 6080 Ak-20% 60299 55787 52156 50695 49579 49237 49108 49005 W 1700 1400 1100 940 770 693 655 616 W 1700 1400 1100 940 770 693 655 616 W 1700 1400 1100 940 770 693 655 616 ENERGY LOSSES E0 D0 C0 B0 A0 A0-10% A0-15% A0-20% 13000 Dk 18692 16064 13436 12034 10545 9871 9538 9196 10500 Ck 17961 15333 12705 11304 9814 9140 8807 8465 Total Losses - Min (kWh) 9000 7600 6840 Bk Ak Ak-10% 17523 17113 16891 14895 14485 14263 12267 11857 11635 10865 10456 10234 9376 8967 8745 8701 8292 8070 8368 7959 7737 8027 7618 7395 6460 Ak-15% 16780 14152 11524 10123 8633 7959 7626 7284 6080 Ak-20% 16669 14041 11413 10012 8522 7848 7515 7173 E0 D0 C0 B0 A0 A0-10% A0-15% A0-20% 13000 Dk 30091 27463 24835 23434 21945 21270 20937 20596 10500 Ck 27168 24540 21912 20511 19022 18347 18014 17673 Total Losses - Base (kWh) 9000 7600 6840 Bk Ak Ak-10% 25415 23778 22889 22787 21150 20261 20159 18522 17633 18757 17120 16232 17268 15631 14742 16593 14956 14068 16260 14624 13735 15919 14282 13393 6460 Ak-15% 22445 19817 17189 15787 14298 13624 13291 12949 6080 Ak-20% 22001 19373 16745 15343 13854 13179 12846 12505 E0 D0 C0 B0 A0 A0-10% A0-15% A0-20% 13000 Dk 41913 39285 36657 35256 33766 33092 32759 32417 10500 Ck 36717 34089 31461 30059 28570 27895 27563 27221 Total Losses - Max (kWh) 9000 7600 6840 Bk Ak Ak-10% 33599 30689 29109 30971 28061 26481 28343 25433 23853 26941 24031 22452 25452 22542 20962 24778 21868 20288 24445 21535 19955 24103 21193 19613 6460 Ak-15% 28319 25691 23063 21662 20173 19498 19165 18824 6080 Ak-20% 27530 24902 22274 20872 19383 18708 18375 18034 W 1700 1400 1100 940 770 693 655 616 W 1700 1400 1100 940 770 693 655 616 W 1700 1400 1100 940 770 693 655 616 XXXII BC3 LIFE CYCLE COST C0 B0 A0 A0-10% A0-15% A0-20% 13000 Bk 59493 59463 59750 59866 59241 58632 Price Energy- Min (€) 11000 9900 9350 8800 Ak Ak-10% Ak-15% Ak-20% 59366 59357 59369 59391 59709 59905 60020 60145 60156 60440 60599 60768 60369 60706 60890 61086 59791 60155 60353 60561 59230 59620 59831 60053 C0 B0 A0 A0-10% A0-15% A0-20% 13000 Bk 91609 86622 84784 83484 81442 79417 Price Energy - Base (€) 11000 9900 9350 8800 Ak Ak-10% Ak-15% Ak-20% 89592 88543 88035 87537 84978 84134 83728 83334 83300 82544 82183 81832 82096 81394 81058 80734 80102 79426 79104 78793 78125 77475 77166 76868 13000 Bk 123725 113780 109818 107102 103644 100202 Price Energy - Base (€) 11000 9900 9350 Ak Ak-10% Ak-15% 119817 117729 116700 110246 108363 107437 106444 104648 103767 103824 102081 101226 100414 98698 97856 97020 95330 94501 W 2800 2100 1800 1620 1530 1440 W 2800 2100 1800 1620 1530 1440 W 2800 2100 1800 1620 1530 1440 ENERGY LOSSES C0 B0 A0 A0-10% A0-15% A0-20% 8800 Ak-20% 115683 106522 102896 100382 97025 93684 C0 B0 A0 A0-10% A0-15% A0-20% 13000 Bk 28328 22196 19568 17816 16064 14312 Total Losses - Min (kWh) 11000 9900 9350 8800 Ak Ak-10% Ak-15% Ak-20% 27743 27422 27261 27100 21611 21290 21129 20968 18983 18662 18501 18340 17231 16910 16749 16588 15479 15158 14997 14836 13727 13406 13245 13084 C0 B0 A0 A0-10% A0-15% A0-20% 13000 Bk 39727 33595 30967 29215 27463 25711 Total Losses - Min (kWh) 11000 9900 9350 8800 Ak Ak-10% Ak-15% Ak-20% 37389 36103 35460 34817 31257 29971 29328 28685 28629 27343 26700 26057 26877 25591 24948 24305 25125 23839 23196 22553 23373 22087 21444 20801 13000 Bk 51549 45417 42789 41037 39285 37533 Total Losses - Min (kWh) 11000 9900 9350 8800 Ak Ak-10% Ak-15% Ak-20% 47392 45106 43962 42819 41260 38974 37830 36687 38632 36346 35202 34059 36880 34594 33450 32307 35128 32842 31698 30555 33376 31090 29946 28803 W 2800 2100 1800 1620 1530 1440 W 2800 2100 1800 1620 1530 1440 W 2800 2100 1800 1620 1530 1440 C0 B0 A0 A0-10% A0-15% A0-20% XXXIII BC4 P0-41 P0-34 P0-28 P0-20 Load factor - Min (kWh) 326000 277100 Pk-326 Pk-277 519272 494598 466055 441381 412838 388164 341882 317208 P0-41 P0-34 P0-28 P0-20 Load factor - Base (kWh) 326000 277100 228200 Pk-326 Pk-277 Pk-228 724886 669371 613855 671669 616154 560638 618452 562937 507421 547496 491981 436465 P0-41 P0-34 P0-28 P0-20 Load factor - Max (kWh) 326000 277100 228200 Pk-326 Pk-277 Pk-228 1382854 1228643 1074432 1329637 1175426 1021215 1276420 1122209 967998 1205464 1051253 897042 P0-41 P0-34 P0-28 P0-20 Electricity Price-Min (€) 326000 277100 Pk-326 Pk-277 724886 669371 671669 616154 618452 562937 547496 491981 P0-41 P0-34 P0-28 P0-20 Electricity Price-Max (€) 326000 277100 228200 Pk-326 Pk-277 Pk-228 724886 669371 613855 671669 616154 560638 618452 562937 507421 547496 491981 436465 W 40500 34425 28350 20250 W 40500 34425 28350 20250 W 40500 34425 28350 20250 W 40500 34425 28350 20250 W 40500 34425 28350 20250 LCC 228200 Pk-228 469924 416707 363490 292534 228200 Pk-228 613855 560638 507421 436465 P0-41 P0-34 P0-28 P0-20 Load factor - Min (kWh) 326000 277100 Pk-326 Pk-277 1192850 1200180 1239363 1294026 1390974 1492969 1756606 1921711 P0-41 P0-34 P0-28 P0-20 Load factor - Base (kWh) 326000 277100 228200 Pk-326 Pk-277 Pk-228 1370625 1351288 1356490 1417138 1445134 1500160 1568749 1644077 1748927 1934380 2072819 2244101 P0-41 P0-34 P0-28 P0-20 Load factor - Max (kWh) 326000 277100 228200 Pk-326 Pk-277 Pk-228 1939504 1834836 1754706 1986017 1928682 1898375 2137628 2127625 2147142 2503260 2556367 2642316 P0-41 P0-34 P0-28 P0-20 Electricity Price-Min (€) 326000 277100 Pk-326 Pk-277 1182603 1177666 1242920 1285316 1408334 1498063 1792370 1945209 P0-41 P0-34 P0-28 P0-20 Electricity Price-Max (€) 326000 277100 228200 Pk-326 Pk-277 Pk-228 1683994 1640658 1621860 1707501 1711498 1742524 1836106 1887435 1968285 2171064 2285503 2432785 W 40500 34425 28350 20250 W 40500 34425 28350 20250 W 40500 34425 28350 20250 W 40500 34425 28350 20250 W 40500 34425 28350 20250 XXXIV 228200 Pk-228 1232048 1375717 1624484 2119658 228200 Pk-228 1197268 1354741 1617312 2130890 BC5 E0 C0 A0 A0-10% A0-15% A0-20% Annual Energy losses Load factor - Min (kWh) 21000 15000 13500 12750 12000 Ck Ak Ak-10% Ak-15% Ak-20% 38654 35369 34547 34137 33726 29894 26609 25787 25377 24966 24200 20915 20093 19683 19272 22929 19644 18823 18412 18002 22294 19009 18188 17777 17367 21659 18374 17553 17142 16732 E0 C0 A0 A0-10% A0-15% A0-20% 21000 Ck 59094 50334 44640 43369 42734 42099 Load factor - Base (kWh) 15000 13500 12750 12000 Ak Ak-10% Ak-15% Ak-20% 49969 47687 46547 45406 41209 38927 37787 36646 35515 33233 32093 30952 34244 31963 30822 29682 33609 31328 30187 29047 32974 30693 29552 28412 E0 C0 A0 A0-10% A0-15% A0-20% 21000 Ck 73146 64386 58692 57422 56787 56152 Load factor - Max (kWh) 15000 13500 12750 12000 Ak Ak-10% Ak-15% Ak-20% 60006 56721 55079 53436 51246 47961 46319 44676 45552 42267 40625 38982 44282 40997 39354 37712 43647 40362 38719 37077 43012 39727 38084 36442 W 3100 2100 1450 1305 1232,5 1160 W 3100 2100 1450 1305 1232,5 1160 W 3100 2100 1450 1305 1232,5 1160 E0 C0 A0 A0-10% A0-15% A0-20% 21000 Ck 169210 137918 118649 114466 112390 110325 Load factor - Min (€) 15000 13500 12750 Ak Ak-10% Ak-15% 159465 157368 156370 130255 128678 127940 112339 111101 110532 108458 107295 106764 106533 105408 104896 104619 103531 103038 12000 Ak-20% 155406 127236 109997 106267 104418 102579 E0 C0 A0 A0-10% A0-15% A0-20% 21000 Ck 249039 217746 198478 194295 192219 190154 Load factor - Base (€) 15000 13500 12750 Ak Ak-10% Ak-15% 216486 208687 204838 187275 179996 176407 169360 162419 159000 165478 158613 155231 163554 156726 153363 161639 154849 151505 12000 Ak-20% 201023 172853 155614 151883 150034 148195 E0 C0 A0 A0-10% A0-15% A0-20% 21000 Ck 303921 272629 253360 249177 247101 245036 Load factor - Max (€) 15000 13500 12750 Ak Ak-10% Ak-15% 255688 243968 238159 226477 215278 209729 208561 197701 192321 204680 193895 188553 202755 192008 186684 200841 190131 184827 12000 Ak-20% 232384 204214 186975 183245 181395 179556 E0 C0 A0 A0-10% A0-15% A0-20% 21000 Ck 225960 198089 181044 177357 175529 173712 Energy Price - Min (€) 15000 13500 12750 Ak Ak-10% Ak-15% 196971 190062 186659 171181 164793 161650 155490 149440 146466 152104 146130 143194 150427 144491 141573 148761 142862 139964 12000 Ak-20% 183289 158541 143526 140291 138690 137099 E0 C0 A0 A0-10% A0-15% A0-20% 21000 Ck 272118 237404 215912 211233 208909 206596 Energy Price - Min (€) 15000 13500 12750 Ak Ak-10% Ak-15% 236001 227311 223017 203369 195199 191165 183230 175398 171533 178853 171096 167269 176680 168961 165153 174517 166837 163047 12000 Ak-20% 218756 187165 167702 163476 161378 159291 W 3100 2100 1450 1305 1232,5 1160 W 3100 2100 1450 1305 1232,5 1160 W 3100 2100 1450 1305 1232,5 1160 Electrity price W 3100 2100 1450 1305 1232,5 1160 E0 C0 A0 A0-10% A0-15% A0-20% W 3100 2100 1450 1305 1232,5 1160 E0 C0 A0 A0-10% A0-15% A0-20% 21000 Ck 59094 50334 44640 43369 42734 42099 Energy Price - Min (kWh) 15000 13500 12750 12000 Ak Ak-10% Ak-15% Ak-20% 49969 47687 46547 45406 41209 38927 37787 36646 35515 33233 32093 30952 34244 31963 30822 29682 33609 31328 30187 29047 32974 30693 29552 28412 21000 Ck 272118 237404 215912 211233 208909 206596 Energy Price - Max (kWh) 15000 13500 12750 12000 Ak Ak-10% Ak-15% Ak-20% 236001 227311 223017 218756 203369 195199 191165 187165 183230 175398 171533 167702 178853 171096 167269 163476 176680 168961 165153 161378 174517 166837 163047 159291 W 3100 2100 1450 1305 1232,5 1160 W 3100 2100 1450 1305 1232,5 1160 XXXV BC6 Total losses Load factor min W 4000 3000 2600 2340 2210 2080 LCC 18000 Bk 44895 36135 32631 30353 29215 28076 Load factor - Min (kWh) 16000 14400 13600 Ak Ak-10% Ak-15% 43800 42924 42486 35040 34164 33726 31536 30660 30222 29258 28382 27944 28120 27244 26806 26981 26105 25667 12800 Ak-20% 42048 33288 29784 27506 26368 25229 Co Bo Ao A0-10% A0-15% A0-20% 18000 Bk 62415 53655 50151 47873 46735 45596 Load factor - Base (kWh) 16000 14400 13600 Ak Ak-10% Ak-15% 59373 56940 55723 50613 48180 46963 47109 44676 43459 44832 42398 41182 43693 41260 40043 42554 40121 38904 12800 Ak-20% 54507 45747 42243 39965 38826 37687 Co Bo Ao A0-10% A0-15% A0-20% 18000 Bk 74460 65700 62196 59918 58780 57641 Load factor - Max (kWh) 16000 14400 13600 Ak Ak-10% Ak-15% 70080 66576 64824 61320 57816 56064 57816 54312 52560 55538 52034 50282 54400 50896 49144 53261 49757 48005 12800 Ak-20% 63072 54312 50808 48530 47392 46253 18000 Bk 62415 53655 50151 47873 46735 45596 Energy Price - Min (kWh) 16000 14400 13600 Ak Ak-10% Ak-15% 59373 56940 55723 50613 48180 46963 47109 44676 43459 44832 42398 41182 43693 41260 40043 42554 40121 38904 12800 Ak-20% 54507 45747 42243 39965 38826 37687 18000 Bk 62415 53655 50151 47873 46735 45596 Energy Price - Max (kWh) 16000 14400 13600 Ak Ak-10% Ak-15% 59373 56940 55723 50613 48180 46963 47109 44676 43459 44832 42398 41182 43693 41260 40043 42554 40121 38904 12800 Ak-20% 54507 45747 42243 39965 38826 37687 Co Bo Ao A0-10% A0-15% A0-20% Co Bo Ao A0-10% A0-15% A0-20% 18000 Bk 133394 116815 110973 107418 105712 104053 Load factor - Min (€) 16000 14400 13600 12800 Ak Ak-10% Ak-15% Ak-20% 131879 130912 130510 130163 116279 116096 116086 116131 110829 110960 111106 111307 107529 107863 108112 108415 105950 106386 106686 107040 104419 104957 105308 105712 Co Bo Ao A0-10% A0-15% A0-20% 18000 Bk 174449 157869 152028 148472 146766 145108 Load factor - Base (€) 16000 14400 13600 12800 Ak Ak-10% Ak-15% Ak-20% 168372 163756 161530 159357 152773 148940 147105 145325 147323 143803 142126 140502 144022 140707 139131 137609 142443 139230 137705 136234 140912 137801 136327 134907 Co Bo Ao A0-10% A0-15% A0-20% 18000 Bk 202674 186095 180253 176698 174992 173333 Load factor - Max (€) 16000 14400 13600 12800 Ak Ak-10% Ak-15% Ak-20% 193461 186336 182855 179429 177862 171520 168431 165396 172412 166384 163451 160573 169111 163287 160456 157680 167533 161810 159031 156305 166002 160381 157652 154978 Co Bo Ao A0-10% A0-15% A0-20% 18000 Bk 101320 95004 93268 92381 92010 91686 Energy Price - Min (€) 16000 14400 13600 12800 Ak Ak-10% Ak-15% Ak-20% 98807 97042 96241 95494 93471 92490 92080 91726 92127 91459 91206 91008 91495 91030 90880 90784 91250 90888 90788 90743 91054 90793 90744 90750 Co Bo Ao A0-10% A0-15% A0-20% 18000 Bk 247578 220735 210787 204564 201523 198531 Energy Price - Max (€) 16000 14400 13600 12800 Ak Ak-10% Ak-15% Ak-20% 237937 230470 226818 223221 212074 205390 202130 198924 202518 196148 193045 189996 196550 190383 187382 184434 193637 187572 184621 181725 190771 184809 181909 179064 W 4000 3000 2600 2340 2210 2080 Load factor base W 4000 3000 2600 2340 2210 2080 W 4000 3000 2600 2340 2210 2080 Electricity price min W 4000 3000 2600 2340 2210 2080 Co Bo Ao A0-10% A0-15% A0-20% W 4000 3000 2600 2340 2210 2080 W 4000 3000 2600 2340 2210 2080 W 4000 3000 2600 2340 2210 2080 Electricity price max W 4000 3000 2600 2340 2210 2080 Co Bo Ao A0-10% A0-15% A0-20% W 4000 3000 2600 2340 2210 2080 XXXVI BC7 LIFE CYCLE COST P0-110 W P0-90 W P0-70 W P0-60 W Price Energy- Min (€) Pk-750 W Pk-600 W Pk-500 W Pk-400 W 2226 2284 2344 2425 2217 2305 2392 2510 2232 2361 2486 2655 2250 2405 2555 2760 P0-110 W P0-90 W P0-70 W P0-60 W Price Energy - Base (€) Pk-750 W Pk-600 W Pk-500 W Pk-400 W 3298 3274 3278 3304 3170 3175 3207 3269 3065 3111 3181 3295 3024 3096 3190 3340 P0-110 W P0-90 W P0-70 W P0-60 W Price Energy - Max (€) Pk-750 W Pk-600 W Pk-500 W Pk-400 W 4371 4263 4212 4183 4123 4046 4022 4028 3899 3862 3876 3935 3798 3786 3826 3920 ENERGY LOSSES P0-110 W P0-90 W P0-70 W P0-60 W Total Losses - Min (kWh) Pk-750 W Pk-600 W Pk-500 W Pk-400 W 1183 1139 1110 1081 1008 964 935 905 832 789 759 730 745 701 672 643 P0-110 W P0-90 W P0-70 W P0-60 W Total Losses - Base (kWh) Pk-750 W Pk-600 W Pk-500 W Pk-400 W 1573 1451 1370 1288 1397 1276 1194 1113 1222 1100 1019 938 1135 1013 932 850 P0-110 W P0-90 W P0-70 W P0-60 W Total Losses - Max (kWh) Pk-750 W Pk-600 W Pk-500 W Pk-400 W 2157 1918 1759 1600 1982 1743 1584 1425 1807 1568 1409 1250 1719 1480 1321 1162 XXXVII ANNEX 6: Life Cycle Cost Shaded Diagram XXXVIII BASE CASE 1 Ck D0 C0 B0 A0 A0-10% A0-15% A0-20% 750 725 700 675 650 625 610 600 575 550 525 520 500 475 450 430 425 400 387 375 366 350 344 325 300 275 250 225 200 4600 0% 2% 4% 6% 8% 9% 10% 11% 12% 14% 15% 15% 16% 16% 17% 18% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% Bk 4550 0% 2% 4% 6% 8% 10% 10% 11% 12% 14% 15% 15% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4500 0% 2% 4% 6% 8% 10% 11% 11% 12% 14% 15% 15% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4450 0% 3% 5% 6% 8% 10% 11% 11% 13% 14% 15% 15% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4400 1% 3% 5% 7% 8% 10% 11% 11% 13% 14% 15% 15% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4350 1% 3% 5% 7% 8% 10% 11% 11% 13% 14% 15% 15% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4300 1% 3% 5% 7% 8% 10% 11% 11% 13% 14% 15% 15% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4250 1% 3% 5% 7% 9% 10% 11% 12% 13% 14% 15% 15% 16% 17% 18% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4200 1% 3% 5% 7% 9% 10% 11% 12% 13% 14% 15% 15% 16% 17% 18% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4150 1% 3% 5% 7% 9% 10% 11% 12% 13% 14% 15% 15% 16% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4100 1% 3% 5% 7% 9% 10% 11% 12% 13% 14% 15% 15% 16% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4050 2% 4% 5% 7% 9% 10% 11% 12% 13% 14% 15% 16% 16% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 4000 2% 4% 6% 7% 9% 11% 11% 12% 13% 14% 15% 16% 16% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 18% 17% 3950 2% 4% 6% 8% 9% 11% 12% 12% 13% 14% 15% 16% 16% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 18% 17% 3900 2% 4% 6% 8% 9% 11% 12% 12% 13% 15% 16% 16% 16% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 3850 2% 4% 6% 8% 9% 11% 12% 12% 13% 15% 16% 16% 16% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% Ak 3800 2% 4% 6% 8% 9% 11% 12% 12% 14% 15% 16% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 3750 2% 4% 6% 8% 10% 11% 12% 12% 14% 15% 16% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 3700 2% 4% 6% 8% 10% 11% 12% 12% 14% 15% 16% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 3650 3% 5% 6% 8% 10% 11% 12% 13% 14% 15% 16% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 3600 3% 5% 7% 8% 10% 11% 12% 13% 14% 15% 16% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 3550 3% 5% 7% 8% 10% 11% 12% 13% 14% 15% 16% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 16% 3500 3% 5% 7% 8% 10% 11% 12% 13% 14% 15% 16% 16% 17% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 16% 3450 3% 5% 7% 9% 10% 12% 12% 13% 14% 15% 16% 16% 17% 18% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 16% 3400 3% 5% 7% 9% 10% 12% 12% 13% 14% 15% 16% 16% 17% 18% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 16% 3350 3% 5% 7% 9% 10% 12% 13% 13% 14% 15% 16% 16% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 16% 3300 3% 5% 7% 9% 10% 12% 13% 13% 14% 15% 16% 16% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 16% 3250 4% 6% 7% 9% 11% 12% 13% 13% 14% 15% 16% 16% 17% 18% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 16% Ak-10% 3200 4% 6% 7% 9% 11% 12% 13% 13% 14% 15% 16% 16% 17% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 18% 17% 16% 3150 4% 6% 8% 9% 11% 12% 13% 13% 14% 16% 16% 17% 17% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 18% 17% 16% 3100 4% 6% 8% 9% 11% 12% 13% 13% 15% 16% 16% 17% 17% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 16% 3050 4% 6% 8% 9% 11% 12% 13% 14% 15% 16% 16% 17% 17% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 16% 3000 4% 6% 8% 9% 11% 12% 13% 14% 15% 16% 17% 17% 17% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 16% 2925 4% 6% 8% 10% 11% 12% 13% 14% 15% 16% 17% 17% 17% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 16% Ak-15% 2950 4% 6% 8% 10% 11% 12% 13% 14% 15% 16% 17% 17% 17% 18% 18% 19% 19% 19% 19% 19% 19% 19% 19% 19% 18% 18% 17% 17% 16% 2900 4% 6% 8% 10% 11% 13% 13% 14% 15% 16% 17% 17% 17% 18% 18% 19% 19% 19% 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18,7% 19,1% 19,5% 2700 5,1% 5,6% 6,0% 6,4% 6,9% 7,3% 7,7% 8,2% 8,6% 9,0% 9,5% 9,9% 10,3% 10,7% 11,2% 11,6% 12,0% 12,4% 12,9% 13,3% 13,7% 14,1% 14,5% 15,0% 15,4% 15,8% 16,2% 16,6% 17,0% 17,4% 17,9% 18,3% 18,7% 19,1% 19,5% 19,9% 20,3% 20,7% 2600 6,4% 6,8% 7,3% 7,7% 8,1% 8,6% 9,0% 9,4% 9,8% 10,3% 10,7% 11,1% 11,5% 12,0% 12,4% 12,8% 13,2% 13,7% 14,1% 14,5% 14,9% 15,3% 15,7% 16,2% 16,6% 17,0% 17,4% 17,8% 18,2% 18,6% 19,0% 19,4% 19,8% 20,3% 20,7% 21,1% 21,5% 21,9% 2500 7,6% 8,1% 8,5% 8,9% 9,4% 9,8% 10,2% 10,6% 11,1% 11,5% 11,9% 12,3% 12,8% 13,2% 13,6% 14,0% 14,4% 14,9% 15,3% 15,7% 16,1% 16,5% 16,9% 17,4% 17,8% 18,2% 18,6% 19,0% 19,4% 19,8% 20,2% 20,6% 21,0% 21,4% 21,8% 22,2% 22,6% 23,0% 2400 8,9% 9,3% 9,7% 10,2% 10,6% 11,0% 11,4% 11,9% 12,3% 12,7% 13,1% 13,6% 14,0% 14,4% 14,8% 15,2% 15,6% 16,1% 16,5% 16,9% 17,3% 17,7% 18,1% 18,5% 18,9% 19,3% 19,8% 20,2% 20,6% 21,0% 21,4% 21,8% 22,2% 22,6% 23,0% 23,4% 23,8% 24,2% 2300 10,1% 10,5% 11,0% 11,4% 11,8% 12,2% 12,7% 13,1% 13,5% 13,9% 14,3% 14,8% 15,2% 15,6% 16,0% 16,4% 16,8% 17,3% 17,7% 18,1% 18,5% 18,9% 19,3% 19,7% 20,1% 20,5% 20,9% 21,3% 21,7% 22,1% 22,5% 22,9% 23,3% 23,7% 24,1% 24,5% 24,9% 25,3% 2200 11,3% 11,8% 12,2% 12,6% 13,0% 13,5% 13,9% 14,3% 14,7% 15,1% 15,5% 16,0% 16,4% 16,8% 17,2% 17,6% 18,0% 18,4% 18,8% 19,2% 19,7% 20,1% 20,5% 20,9% 21,3% 21,7% 22,1% 22,5% 22,9% 23,3% 23,7% 24,1% 24,5% 24,8% 25,2% 25,6% 26,0% 26,4% 2100 12,6% 13,0% 13,4% 13,8% 14,2% 14,7% 15,1% 15,5% 15,9% 16,3% 16,7% 17,2% 17,6% 18,0% 18,4% 18,8% 19,2% 19,6% 20,0% 20,4% 20,8% 21,2% 21,6% 22,0% 22,4% 22,8% 23,2% 23,6% 24,0% 24,4% 24,8% 25,2% 25,6% 26,0% 26,4% 26,8% 27,1% 27,5% 2000 13,8% 14,2% 14,6% 15,0% 15,4% 15,9% 16,3% 16,7% 17,1% 17,5% 17,9% 18,3% 18,7% 19,2% 19,6% 20,0% 20,4% 20,8% 21,2% 21,6% 22,0% 22,4% 22,8% 23,2% 23,6% 24,0% 24,4% 24,8% 25,1% 25,5% 25,9% 26,3% 26,7% 27,1% 27,5% 27,9% 28,3% 28,6% 1900 15,0% 15,4% 15,8% 16,2% 16,6% 17,1% 17,5% 17,9% 18,3% 18,7% 19,1% 19,5% 19,9% 20,3% 20,7% 21,1% 21,5% 21,9% 22,3% 22,7% 23,1% 23,5% 23,9% 24,3% 24,7% 25,1% 25,5% 25,9% 26,3% 26,7% 27,1% 27,4% 27,8% 28,2% 28,6% 29,0% 29,4% 29,7% 1800 16,2% 16,6% 17,0% 17,4% 17,8% 18,2% 18,6% 19,1% 19,5% 19,9% 20,3% 20,7% 21,1% 21,5% 21,9% 22,3% 22,7% 23,1% 23,5% 23,9% 24,3% 24,7% 25,1% 25,4% 25,8% 26,2% 26,6% 27,0% 27,4% 27,8% 28,2% 28,5% 28,9% 29,3% 29,7% 30,1% 30,5% 30,8% 1700 17,4% 17,8% 18,2% 18,6% 19,0% 19,4% 19,8% 20,2% 20,6% 21,0% 21,4% 21,8% 22,2% 22,6% 23,0% 23,4% 23,8% 24,2% 24,6% 25,0% 25,4% 25,8% 26,2% 26,6% 27,0% 27,3% 27,7% 28,1% 28,5% 28,9% 29,3% 29,6% 30,0% 30,4% 30,8% 31,2% 31,5% 31,9% 1600 18,5% 19,0% 19,4% 19,8% 20,2% 20,6% 21,0% 21,4% 21,8% 22,2% 22,6% 23,0% 23,4% 23,8% 24,2% 24,6% 25,0% 25,4% 25,7% 26,1% 26,5% 26,9% 27,3% 27,7% 28,1% 28,5% 28,8% 29,2% 29,6% 30,0% 30,4% 30,7% 31,1% 31,5% 31,9% 32,2% 32,6% 33,0% 1500 19,7% 20,1% 20,5% 20,9% 21,3% 21,7% 22,1% 22,5% 22,9% 23,3% 23,7% 24,1% 24,5% 24,9% 25,3% 25,7% 26,1% 26,5% 26,9% 27,3% 27,6% 28,0% 28,4% 28,8% 29,2% 29,6% 29,9% 30,3% 30,7% 31,1% 31,5% 31,8% 32,2% 32,6% 33,0% 33,3% 33,7% 34,1% 1450 20,3% 20,7% 21,1% 21,5% 21,9% 22,3% 22,7% 23,1% 23,5% 23,9% 24,3% 24,7% 25,1% 25,5% 25,9% 26,3% 26,6% 27,0% 27,4% 27,8% 28,2% 28,6% 29,0% 29,3% 29,7% 30,1% 30,5% 30,9% 31,2% 31,6% 32,0% 32,4% 32,7% 33,1% 33,5% 33,9% 34,2% 34,6% 1400 20,9% 21,3% 21,7% 22,1% 22,5% 22,9% 23,3% 23,7% 24,1% 24,5% 24,9% 25,3% 25,6% 26,0% 26,4% 26,8% 27,2% 27,6% 28,0% 28,4% 28,7% 29,1% 29,5% 29,9% 30,3% 30,7% 31,0% 31,4% 31,8% 32,2% 32,5% 32,9% 33,3% 33,7% 34,0% 34,4% 34,8% 35,1% 1305 22,0% 22,4% 22,8% 23,2% 23,6% 24,0% 24,4% 24,8% 25,2% 25,5% 25,9% 26,3% 26,7% 27,1% 27,5% 27,9% 28,3% 28,6% 29,0% 29,4% 29,8% 30,2% 30,6% 30,9% 31,3% 31,7% 32,1% 32,4% 32,8% 33,2% 33,6% 33,9% 34,3% 34,7% 35,0% 35,4% 35,8% 36,1% 1300 22,0% 22,4% 22,8% 23,2% 23,6% 24,0% 24,4% 24,8% 25,2% 25,6% 26,0% 26,4% 26,8% 27,2% 27,5% 27,9% 28,3% 28,7% 29,1% 29,5% 29,8% 30,2% 30,6% 31,0% 31,4% 31,7% 32,1% 32,5% 32,9% 33,2% 33,6% 34,0% 34,3% 34,7% 35,1% 35,4% 35,8% 36,2% 1233 22,8% 23,2% 23,6% 24,0% 24,4% 24,8% 25,2% 25,6% 26,0% 26,4% 26,7% 27,1% 27,5% 27,9% 28,3% 28,7% 29,1% 29,4% 29,8% 30,2% 30,6% 31,0% 31,3% 31,7% 32,1% 32,5% 32,8% 33,2% 33,6% 34,0% 34,3% 34,7% 35,1% 35,4% 35,8% 36,2% 36,5% 36,9% 1200 23,2% 23,6% 24,0% 24,4% 24,8% 25,2% 25,6% 25,9% 26,3% 26,7% 27,1% 27,5% 27,9% 28,3% 28,7% 29,0% 29,4% 29,8% 30,2% 30,6% 30,9% 31,3% 31,7% 32,1% 32,4% 32,8% 33,2% 33,6% 33,9% 34,3% 34,7% 35,0% 35,4% 35,8% 36,1% 36,5% 36,9% 37,2% 1160 23,6% 24,0% 24,4% 24,8% 25,2% 25,6% 26,0% 26,4% 26,8% 27,2% 27,6% 27,9% 28,3% 28,7% 29,1% 29,5% 29,9% 30,2% 30,6% 31,0% 31,4% 31,8% 32,1% 32,5% 32,9% 33,2% 33,6% 34,0% 34,4% 34,7% 35,1% 35,5% 35,8% 36,2% 36,6% 36,9% 37,3% 37,6% 1100 24,3% 24,7% 25,1% 25,5% 25,9% 26,3% 26,7% 27,1% 27,5% 27,8% 28,2% 28,6% 29,0% 29,4% 29,8% 30,1% 30,5% 30,9% 31,3% 31,6% 32,0% 32,4% 32,8% 33,1% 33,5% 33,9% 34,3% 34,6% 35,0% 35,4% 35,7% 36,1% 36,5% 36,8% 37,2% 37,5% 37,9% 38,3% 1000 25,5% 25,9% 26,2% 26,6% 27,0% 27,4% 27,8% 28,2% 28,6% 28,9% 29,3% 29,7% 30,1% 30,5% 30,8% 31,2% 31,6% 32,0% 32,4% 32,7% 33,1% 33,5% 33,8% 34,2% 34,6% 35,0% 35,3% 35,7% 36,0% 36,4% 36,8% 37,1% 37,5% 37,9% 38,2% 38,6% 38,9% 39,3% 900 26,6% 27,0% 27,4% 27,7% 28,1% 28,5% 28,9% 29,3% 29,7% 30,0% 30,4% 30,8% 31,2% 31,6% 31,9% 32,3% 32,7% 33,1% 33,4% 33,8% 34,2% 34,5% 34,9% 35,3% 35,6% 36,0% 36,4% 36,7% 37,1% 37,5% 37,8% 38,2% 38,5% 38,9% 39,2% 39,6% 40,0% 40,3% Ak-10% 13500 13400 13200 13000 12800 16,2% 16,4% 16,8% 17,2% 17,6% 17,4% 17,6% 18,0% 18,4% 18,8% 18,6% 18,8% 19,2% 19,6% 20,0% 19,7% 19,9% 20,4% 20,8% 21,2% 20,9% 21,1% 21,5% 21,9% 22,3% 22,1% 22,3% 22,7% 23,1% 23,5% 23,2% 23,4% 23,8% 24,2% 24,6% 24,4% 24,5% 24,9% 25,3% 25,7% 25,5% 25,7% 26,1% 26,5% 26,8% 26,6% 26,8% 27,2% 27,6% 28,0% 27,7% 27,9% 28,3% 28,7% 29,1% 28,8% 29,0% 29,4% 29,8% 30,2% 29,9% 30,1% 30,5% 30,9% 31,3% 31,0% 31,2% 31,6% 32,0% 32,3% 32,1% 32,3% 32,7% 33,0% 33,4% 33,2% 33,4% 33,7% 34,1% 34,5% 34,3% 34,4% 34,8% 35,2% 35,5% 34,8% 35,0% 35,3% 35,7% 36,1% 35,3% 35,5% 35,9% 36,2% 36,6% 36,3% 36,5% 36,9% 37,2% 37,6% 36,4% 36,5% 36,9% 37,3% 37,6% 37,1% 37,2% 37,6% 38,0% 38,3% 37,4% 37,6% 37,9% 38,3% 38,7% 37,8% 38,0% 38,4% 38,7% 39,1% 38,4% 38,6% 39,0% 39,3% 39,7% 39,5% 39,6% 40,0% 40,4% 40,7% 40,5% 40,7% 41,0% 41,4% 41,7% Ak-15% 12750 12600 17,7% 18,1% 18,9% 19,2% 20,1% 20,4% 21,3% 21,6% 22,4% 22,7% 23,6% 23,9% 24,7% 25,0% 25,8% 26,1% 26,9% 27,2% 28,1% 28,3% 29,2% 29,5% 30,3% 30,5% 31,4% 31,6% 32,4% 32,7% 33,5% 33,8% 34,6% 34,8% 35,6% 35,9% 36,2% 36,4% 36,7% 37,0% 37,7% 37,9% 37,7% 38,0% 38,4% 38,7% 38,8% 39,0% 39,2% 39,4% 39,8% 40,0% 40,8% 41,1% 41,8% 42,1% XXIII Ak-20% 12000 19,3% 20,4% 21,6% 22,8% 23,9% 25,0% 26,2% 27,3% 28,4% 29,5% 30,6% 31,7% 32,8% 33,8% 34,9% 35,9% 37,0% 37,5% 38,0% 39,0% 39,1% 39,8% 40,1% 40,5% 41,1% 42,1% 43,1% BC6 C0 B0 A0 A0-10% A0-15% A0-20% Bk 4000 3880 3760 3640 3520 3400 3280 3160 3040 3000 2920 2800 2680 2600 2560 2440 2340 2320 2210 2200 2080 1960 1840 1720 1600 1480 1360 18000 0,0% 1,2% 2,4% 3,6% 4,8% 5,9% 7,0% 8,1% 9,2% 9,5% 10,2% 11,2% 12,2% 12,9% 13,2% 14,1% 14,9% 15,0% 15,9% 15,9% 16,8% 17,7% 18,5% 19,3% 20,1% 20,9% 21,6% Ak 17900 0,2% 1,4% 2,6% 3,8% 4,9% 6,1% 7,2% 8,2% 9,3% 9,7% 10,3% 11,4% 12,3% 13,0% 13,3% 14,3% 15,0% 15,2% 16,0% 16,1% 16,9% 17,8% 18,6% 19,4% 20,2% 21,0% 21,7% 17800 0,4% 1,6% 2,8% 3,9% 5,1% 6,2% 7,3% 8,4% 9,5% 9,8% 10,5% 11,5% 12,5% 13,1% 13,4% 14,4% 15,2% 15,3% 16,1% 16,2% 17,1% 17,9% 18,7% 19,5% 20,3% 21,1% 21,8% 17700 0,5% 1,8% 2,9% 4,1% 5,3% 6,4% 7,5% 8,6% 9,6% 10,0% 10,6% 11,6% 12,6% 13,3% 13,6% 14,5% 15,3% 15,4% 16,3% 16,3% 17,2% 18,0% 18,9% 19,7% 20,4% 21,2% 21,9% 17600 0,7% 1,9% 3,1% 4,3% 5,4% 6,5% 7,6% 8,7% 9,8% 10,1% 10,8% 11,8% 12,8% 13,4% 13,7% 14,7% 15,4% 15,6% 16,4% 16,5% 17,3% 18,2% 19,0% 19,8% 20,5% 21,3% 22,0% 17500 0,9% 2,1% 3,3% 4,4% 5,6% 6,7% 7,8% 8,9% 9,9% 10,3% 10,9% 11,9% 12,9% 13,5% 13,9% 14,8% 15,5% 15,7% 16,5% 16,6% 17,4% 18,3% 19,1% 19,9% 20,6% 21,4% 22,1% 17400 1,1% 2,3% 3,5% 4,6% 5,7% 6,9% 7,9% 9,0% 10,1% 10,4% 11,1% 12,1% 13,0% 13,7% 14,0% 14,9% 15,7% 15,8% 16,6% 16,7% 17,6% 18,4% 19,2% 20,0% 20,8% 21,5% 22,2% 17300 1,2% 2,4% 3,6% 4,8% 5,9% 7,0% 8,1% 9,2% 10,2% 10,5% 11,2% 12,2% 13,2% 13,8% 14,1% 15,1% 15,8% 16,0% 16,8% 16,8% 17,7% 18,5% 19,3% 20,1% 20,9% 21,6% 22,3% 17200 1,4% 2,6% 3,8% 4,9% 6,1% 7,2% 8,3% 9,3% 10,4% 10,7% 11,4% 12,4% 13,3% 14,0% 14,3% 15,2% 15,9% 16,1% 16,9% 17,0% 17,8% 18,6% 19,4% 20,2% 21,0% 21,7% 22,4% 17100 1,6% 2,8% 4,0% 5,1% 6,2% 7,3% 8,4% 9,5% 10,5% 10,8% 11,5% 12,5% 13,5% 14,1% 14,4% 15,3% 16,1% 16,2% 17,0% 17,1% 17,9% 18,7% 19,5% 20,3% 21,1% 21,8% 22,5% 17000 1,8% 3,0% 4,1% 5,3% 6,4% 7,5% 8,6% 9,6% 10,7% 11,0% 11,7% 12,6% 13,6% 14,2% 14,5% 15,4% 16,2% 16,3% 17,1% 17,2% 18,0% 18,9% 19,7% 20,4% 21,2% 21,9% 22,6% 16900 1,9% 3,1% 4,3% 5,4% 6,6% 7,7% 8,7% 9,8% 10,8% 11,1% 11,8% 12,8% 13,7% 14,4% 14,7% 15,6% 16,3% 16,5% 17,3% 17,3% 18,2% 19,0% 19,8% 20,5% 21,3% 22,0% 22,7% 16800 2,1% 3,3% 4,5% 5,6% 6,7% 7,8% 8,9% 9,9% 10,9% 11,3% 11,9% 12,9% 13,9% 14,5% 14,8% 15,7% 16,4% 16,6% 17,4% 17,4% 18,3% 19,1% 19,9% 20,7% 21,4% 22,1% 22,8% 16700 2,3% 3,5% 4,6% 5,8% 6,9% 8,0% 9,0% 10,1% 11,1% 11,4% 12,1% 13,1% 14,0% 14,6% 14,9% 15,8% 16,6% 16,7% 17,5% 17,6% 18,4% 19,2% 20,0% 20,8% 21,5% 22,2% 22,9% 16600 2,5% 3,6% 4,8% 5,9% 7,0% 8,1% 9,2% 10,2% 11,2% 11,6% 12,2% 13,2% 14,1% 14,8% 15,1% 16,0% 16,7% 16,8% 17,6% 17,7% 18,5% 19,3% 20,1% 20,9% 21,6% 22,3% 23,0% 16500 2,6% 3,8% 5,0% 6,1% 7,2% 8,3% 9,3% 10,4% 11,4% 11,7% 12,4% 13,3% 14,3% 14,9% 15,2% 16,1% 16,8% 17,0% 17,7% 17,8% 18,6% 19,4% 20,2% 21,0% 21,7% 22,4% 23,1% 16400 2,8% 4,0% 5,1% 6,2% 7,4% 8,4% 9,5% 10,5% 11,5% 11,9% 12,5% 13,5% 14,4% 15,0% 15,3% 16,2% 16,9% 17,1% 17,9% 17,9% 18,8% 19,6% 20,3% 21,1% 21,8% 22,5% 23,2% 16300 3,0% 4,1% 5,3% 6,4% 7,5% 8,6% 9,6% 10,7% 11,7% 12,0% 12,7% 13,6% 14,5% 15,2% 15,5% 16,3% 17,1% 17,2% 18,0% 18,1% 18,9% 19,7% 20,4% 21,2% 21,9% 22,6% 23,3% 16200 3,1% 4,3% 5,5% 6,6% 7,7% 8,7% 9,8% 10,8% 11,8% 12,1% 12,8% 13,7% 14,7% 15,3% 15,6% 16,5% 17,2% 17,3% 18,1% 18,2% 19,0% 19,8% 20,6% 21,3% 22,0% 22,7% 23,4% 16100 3,3% 4,5% 5,6% 6,7% 7,8% 8,9% 9,9% 11,0% 12,0% 12,3% 12,9% 13,9% 14,8% 15,4% 15,7% 16,6% 17,3% 17,5% 18,2% 18,3% 19,1% 19,9% 20,7% 21,4% 22,1% 22,8% 23,5% 16000 3,5% 4,6% 5,8% 6,9% 8,0% 9,0% 10,1% 11,1% 12,1% 12,4% 13,1% 14,0% 14,9% 15,5% 15,8% 16,7% 17,4% 17,6% 18,3% 18,4% 19,2% 20,0% 20,8% 21,5% 22,2% 22,9% 23,6% Ak-10% 15900 3,7% 4,8% 5,9% 7,0% 8,1% 9,2% 10,2% 11,2% 12,2% 12,6% 13,2% 14,2% 15,1% 15,7% 16,0% 16,9% 17,6% 17,7% 18,5% 18,5% 19,3% 20,1% 20,9% 21,6% 22,3% 23,0% 23,7% 15800 3,8% 5,0% 6,1% 7,2% 8,3% 9,3% 10,4% 11,4% 12,4% 12,7% 13,3% 14,3% 15,2% 15,8% 16,1% 17,0% 17,7% 17,8% 18,6% 18,7% 19,5% 20,2% 21,0% 21,7% 22,4% 23,1% 23,8% 15700 4,0% 5,1% 6,3% 7,4% 8,4% 9,5% 10,5% 11,5% 12,5% 12,8% 13,5% 14,4% 15,3% 15,9% 16,2% 17,1% 17,8% 17,9% 18,7% 18,8% 19,6% 20,3% 21,1% 21,8% 22,5% 23,2% 23,9% 15600 4,2% 5,3% 6,4% 7,5% 8,6% 9,6% 10,7% 11,7% 12,7% 13,0% 13,6% 14,6% 15,5% 16,1% 16,4% 17,2% 17,9% 18,1% 18,8% 18,9% 19,7% 20,5% 21,2% 21,9% 22,6% 23,3% 24,0% 15500 4,3% 5,5% 6,6% 7,7% 8,8% 9,8% 10,8% 11,8% 12,8% 13,1% 13,8% 14,7% 15,6% 16,2% 16,5% 17,3% 18,0% 18,2% 18,9% 19,0% 19,8% 20,6% 21,3% 22,0% 22,7% 23,4% 24,1% 15400 4,5% 5,6% 6,7% 7,8% 8,9% 9,9% 11,0% 12,0% 12,9% 13,3% 13,9% 14,8% 15,7% 16,3% 16,6% 17,5% 18,2% 18,3% 19,1% 19,1% 19,9% 20,7% 21,4% 22,1% 22,8% 23,5% 24,2% 15300 4,7% 5,8% 6,9% 8,0% 9,1% 10,1% 11,1% 12,1% 13,1% 13,4% 14,0% 15,0% 15,9% 16,4% 16,7% 17,6% 18,3% 18,4% 19,2% 19,2% 20,0% 20,8% 21,5% 22,2% 22,9% 23,6% 24,2% 15200 4,8% 6,0% 7,1% 8,1% 9,2% 10,2% 11,3% 12,3% 13,2% 13,5% 14,2% 15,1% 16,0% 16,6% 16,9% 17,7% 18,4% 18,5% 19,3% 19,3% 20,1% 20,9% 21,6% 22,3% 23,0% 23,7% 24,3% 15100 5,0% 6,1% 7,2% 8,3% 9,4% 10,4% 11,4% 12,4% 13,4% 13,7% 14,3% 15,2% 16,1% 16,7% 17,0% 17,8% 18,5% 18,7% 19,4% 19,5% 20,2% 21,0% 21,7% 22,4% 23,1% 23,8% 24,4% 15000 5,2% 6,3% 7,4% 8,5% 9,5% 10,5% 11,6% 12,5% 13,5% 13,8% 14,4% 15,4% 16,2% 16,8% 17,1% 18,0% 18,6% 18,8% 19,5% 19,6% 20,4% 21,1% 21,8% 22,5% 23,2% 23,9% 24,5% 14900 5,3% 6,4% 7,5% 8,6% 9,7% 10,7% 11,7% 12,7% 13,6% 13,9% 14,6% 15,5% 16,4% 16,9% 17,2% 18,1% 18,8% 18,9% 19,6% 19,7% 20,5% 21,2% 21,9% 22,6% 23,3% 24,0% 24,6% 14800 5,5% 6,6% 7,7% 8,8% 9,8% 10,8% 11,8% 12,8% 13,8% 14,1% 14,7% 15,6% 16,5% 17,1% 17,4% 18,2% 18,9% 19,0% 19,7% 19,8% 20,6% 21,3% 22,0% 22,7% 23,4% 24,1% 24,7% 14700 5,6% 6,8% 7,8% 8,9% 10,0% 11,0% 12,0% 13,0% 13,9% 14,2% 14,8% 15,7% 16,6% 17,2% 17,5% 18,3% 19,0% 19,1% 19,9% 19,9% 20,7% 21,4% 22,1% 22,8% 23,5% 24,2% 24,8% 14600 5,8% 6,9% 8,0% 9,1% 10,1% 11,1% 12,1% 13,1% 14,0% 14,4% 15,0% 15,9% 16,7% 17,3% 17,6% 18,4% 19,1% 19,2% 20,0% 20,0% 20,8% 21,5% 22,2% 22,9% 23,6% 24,3% 24,9% 14500 6,0% 7,1% 8,2% 9,2% 10,3% 11,3% 12,3% 13,2% 14,2% 14,5% 15,1% 16,0% 16,9% 17,4% 17,7% 18,6% 19,2% 19,4% 20,1% 20,1% 20,9% 21,6% 22,3% 23,0% 23,7% 24,3% 25,0% 14400 6,1% 7,2% 8,3% 9,4% 10,4% 11,4% 12,4% 13,4% 14,3% 14,6% 15,2% 16,1% 17,0% 17,6% 17,8% 18,7% 19,3% 19,5% 20,2% 20,3% 21,0% 21,7% 22,4% 23,1% 23,8% 24,4% 25,1% Ak-15% Ak-20% 14300 6,3% 7,4% 8,5% 9,5% 10,6% 11,6% 12,5% 13,5% 14,4% 14,8% 15,4% 16,3% 17,1% 17,7% 18,0% 18,8% 19,5% 19,6% 20,3% 20,4% 21,1% 21,8% 22,5% 23,2% 23,9% 24,5% 25,1% 14200 6,5% 7,5% 8,6% 9,7% 10,7% 11,7% 12,7% 13,6% 14,6% 14,9% 15,5% 16,4% 17,2% 17,8% 18,1% 18,9% 19,6% 19,7% 20,4% 20,5% 21,2% 21,9% 22,6% 23,3% 24,0% 24,6% 25,2% 14100 6,6% 7,7% 8,8% 9,8% 10,8% 11,9% 12,8% 13,8% 14,7% 15,0% 15,6% 16,5% 17,4% 17,9% 18,2% 19,0% 19,7% 19,8% 20,5% 20,6% 21,3% 22,1% 22,7% 23,4% 24,1% 24,7% 25,3% 14000 6,8% 7,9% 8,9% 10,0% 11,0% 12,0% 13,0% 13,9% 14,8% 15,2% 15,8% 16,6% 17,5% 18,1% 18,3% 19,1% 19,8% 19,9% 20,6% 20,7% 21,4% 22,2% 22,8% 23,5% 24,2% 24,8% 25,4% 13900 6,9% 8,0% 9,1% 10,1% 11,1% 12,1% 13,1% 14,1% 15,0% 15,3% 15,9% 16,8% 17,6% 18,2% 18,4% 19,3% 19,9% 20,0% 20,7% 20,8% 21,5% 22,3% 22,9% 23,6% 24,3% 24,9% 25,5% 13800 7,1% 8,2% 9,2% 10,3% 11,3% 12,3% 13,2% 14,2% 15,1% 15,4% 16,0% 16,9% 17,7% 18,3% 18,6% 19,4% 20,0% 20,2% 20,8% 20,9% 21,6% 22,4% 23,0% 23,7% 24,4% 25,0% 25,6% XXIV 13600 7,4% 8,5% 9,5% 10,6% 11,6% 12,6% 13,5% 14,5% 15,4% 15,7% 16,3% 17,1% 18,0% 18,5% 18,8% 19,6% 20,2% 20,4% 21,1% 21,1% 21,9% 22,6% 23,2% 23,9% 24,5% 25,1% 25,7% 12800 8,7% 9,7% 10,7% 11,7% 12,7% 13,7% 14,6% 15,5% 16,4% 16,7% 17,3% 18,1% 18,9% 19,5% 19,7% 20,5% 21,1% 21,2% 21,9% 22,0% 22,7% 23,3% 24,0% 24,6% 25,2% 25,8% 26,4% BC7 110 107,5 105 102,5 100 97,5 95 92,5 90 87,5 85 82,5 80 77,5 75 72,5 70 67,5 65 62,5 60 57,5 55 750 0% 0% 1% 1% 2% 2% 2% 3% 3% 4% 4% 4% 5% 5% 5% 6% 6% 6% 6% 7% 7% 7% 7% 740 0% 1% 1% 2% 2% 2% 3% 3% 3% 4% 4% 5% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 8% 730 1% 1% 1% 2% 2% 3% 3% 3% 4% 4% 4% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 7% 8% 720 1% 1% 2% 2% 2% 3% 3% 4% 4% 4% 5% 5% 5% 6% 6% 6% 6% 7% 7% 7% 7% 8% 8% 710 1% 2% 2% 2% 3% 3% 3% 4% 4% 5% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 700 1% 2% 2% 3% 3% 3% 4% 4% 4% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 7% 8% 8% 8% 690 2% 2% 2% 3% 3% 4% 4% 4% 5% 5% 5% 6% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 680 2% 2% 3% 3% 3% 4% 4% 5% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 670 2% 3% 3% 3% 4% 4% 4% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 660 2% 3% 3% 4% 4% 4% 5% 5% 5% 6% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 650 3% 3% 3% 4% 4% 5% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 640 3% 3% 4% 4% 4% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 630 3% 4% 4% 4% 5% 5% 5% 6% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 620 3% 4% 4% 5% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 8% 610 4% 4% 4% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 600 4% 4% 5% 5% 5% 6% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 8% 9% 590 4% 5% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 580 4% 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 9% 570 5% 5% 5% 6% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 560 5% 5% 5% 6% 6% 6% 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 550 5% 5% 6% 6% 6% 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 9% 8% 8% 540 5% 6% 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 530 5% 6% 6% 6% 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 520 6% 6% 6% 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 9% 8% 8% 8% 8% 510 6% 6% 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 500 6% 6% 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 490 6% 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 9% 8% 8% 8% 8% 8% 8% 480 6% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 470 7% 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 8% 460 7% 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 9% 8% 8% 8% 8% 8% 8% 8% 7% 450 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 7% 7% 440 7% 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 8% 7% 7% 430 7% 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 9% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 420 7% 8% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 6% 410 7% 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 6% 400 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 9% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 6% 6% 390 8% 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 6% 6% 6% 380 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 6% 6% 5% 370 8% 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 6% 6% 5% 5% 360 8% 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 6% 6% 6% 5% 4% 350 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 6% 6% 5% 5% 4% 340 8% 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 6% 6% 5% 5% 4% 4% XXV 330 8% 8% 8% 8% 9% 9% 8% 8% 8% 8% 8% 8% 8% 7% 7% 7% 6% 6% 6% 5% 4% 4% 3% ANNEX 7: Environmental Impacts (VITO & BIOIS, 2011) The transformer use phase is by far the most impacting stage of the life cycle in terms of energy consumption, water consumption, greenhouse gases emissions and acidification. The production phase has a significant contribution to the following impacts: generation of non-hazardous waste, Volatile Organic Compounds, Persistent Organic Pollutants, Polycyclic Aromatic Hydrocarbons emissions and eutrophication. Finally, the end-of-life phase is significant for the generation of hazardous waste, the particulate matter emissions and the eutrophication, either due to mineral oil or resin. Life Cycle Environmental Impacts Base-case 1: Distribution transformer The total energy consumption for the whole life cycle of the distribution transformer base-case is 3.41 TJ, of which 3.32 TJ (i.e. 316 MWh19) electricity. In the next graph we can see the contribution of each life cycle phase to each impact. 19 The MEEuP specifies a value of 10.5 MJ/kWhe, for electricity from the public grid. XXIII Figure 36 - Distribution of environmental impacts of BC 1 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). Within the production phase, the impacts due to the manufacturing processes are very low (maximum of 2 % for eutrophication). However, the extraction and production of raw material significantly contributes to some emissions, such as volatile organic compounds (VOC) (24%), persistent organic pollutants (POP) (43%) eutrophication (50%) or polycyclic aromatic hydrocarbons (PAHs) (52%), as well as to the generation of non-hazardous waste because of the high steel and copper content (53%). Core steel is the main material responsible for POP emissions. Aluminium and oil induce high PAHs impacts. The use phase accounts for 97% of the energy consumption over the whole life cycle, more than 99.5% of the electricity use and 96.7% of the greenhouse gases emissions. These impacts are almost exclusively due to the electricity losses during the use phase, with maintenance and spare parts impacts being negligible. The distribution phase is negligible for all impacts except for Particulate Matter (PM) for which it accounts for around 13% of the emissions because of the transformer transportation. Finally, the end-of-life accounts for 78% of the hazardous waste generated, 42% of PM emissions to the air, 22% of the eutrophication impacts and 7% of heavy metals emissions. For all other impacts, it has a negligible influence. The incineration of oil is the main reason for the XXIV high contributions to hazardous waste, PM and eutrophication, even if it also reduces slightly the energy consumption over the whole life cycle because of the energy recovery process. Base-case 2: Industry oil transformer The total energy consumption for the whole life cycle of this transformer base-case is 7.34 TJ, of which 7.16 TJ (i.e. 682 MWh) electricity. In the next graph we can see the contribution of each life cycle phase to each impact. Figure 37 - Distribution of environmental impacts of BC 2 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). Within the production phase, the impacts due to the manufacturing processes are very low (maximum of 2% for eutrophication). However, the extraction and production of raw material significantly contributes to some emissions, such as VOC (22%), POP (40%) or PAHs (52%), as well as to the generation of non-hazardous waste because of the high steel and copper content (53%). Core steel is the main material responsible for POP emissions while aluminium and oil induce high PAHs impacts. Eutrophication level is due to coatings, paper, core steel and copper wire. The use phase accounts for 97.1% of the energy consumption over the whole life cycle, 99.6% of the electricity use and 97% of the greenhouse gases emissions. These impacts are XXV almost exclusively due to the electricity losses during the use phase, the maintenance and spare parts impacts being negligible. The distribution phase is negligible for all impacts except for Particulate Matter (PM) for which it accounts for around 10% of the emissions because of the transformer transportation. Finally, the end-of-life accounts for 75% of the hazardous waste generated, 42% of PM emissions to the air, 23% of the eutrophication impacts and 6% of heavy metals emissions. For all other impacts, it has a negligible influence. The incineration of oil is the main reason for the contributions to hazardous waste, PM and HM, even if it also reduces slightly the energy consumption over the whole life cycle because of the energy recovery process. Base-case 3: Industry dry transformer The total energy consumption for the whole life cycle of the dry-type transformer basecase is 12.83 TJ, of which 12.58 TJ (i.e. 1.2 GWh) electricity. In the next graph we can see the contribution of each life cycle phase to each impact. Figure 38 - Distribution of environmental impacts of BC 3 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). XXVI Within the production phase, the manufacturing impacts are very small and the material extraction and production are responsible for the important contribution of this phase to the quantity of landfilled waste (32%) because of the high metal content. Also, core steel highly contributes to the important percentage of this phase in terms of POP emissions (38%) and eutrophication (76%) while aluminium results in high PAHs emissions (58%). As expected, the use phase is the main contributor with over 97% of all the following impacts: total energy (98%) and electricity consumption (99.7%), water for processing, greenhouse gases emissions and acidification. The smallest contributions occur for eutrophication (20%) and PAHs (42%). The electricity losses are the only reason for these impacts as the contribution of maintenance, spare parts or kilometres over product life are negligible in comparison. The distribution is negligible for all impacts except for Particulate Matter (PM) for which it accounts for around 8% of the emissions because of the transformer transportation. The end-of-life is only significant for the hazardous and incinerated waste impact (36%) because of the incineration of epoxy resign and other plastics materials during the end-of-life management. Both incineration and disposal of waste are responsible for the contribution of this phase to PM (16%) and eutrophication impacts (4%). Base-case 4: Power transformer The total energy consumption for the whole life cycle of the power transformer basecase is 172.9 TJ, of which 164.8 TJ (i.e. 15.7 GWh) electricity. In the next graph we can see the contribution of each life cycle phase to each impact. XXVII Figure 39 - Distribution of environmental impacts of BC 4 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). Within the production phase, the impacts due to the manufacturing processes are very low (maximum of 3% for eutrophication). However, the extraction and production of raw material significantly contributes to some emissions, such as VOC (38%), POP (53%) or PAHs (66%), as well as to the generation of non-hazardous waste because of the high steel and copper content (69%). Core steel is the main material responsible for POP emissions while mineral oil results in high levels of VOC and PAHs. The use phase is overwhelming for energy (95%) and electricity (99.3%) consumption, which is again only due the electricity losses during the lifetime and not to maintenance or spare parts. In terms of emissions, its contribution varies between 22% for PM and 94% for GWP, and also represents around 46% of POP and 61% of HM emissions. The distribution phase is negligible for all impacts except for PM for which it accounts for around 15% of the emissions because of the transformer transportation. Finally, the end-of-life accounts for 88% of the hazardous waste generated, 57% of PM emissions to the air, 33% of the eutrophication impacts and 11% of heavy metals emissions. For all other impacts, it has a negligible influence. The incineration of oil is the main reason for the XXVIII high contributions to hazardous waste, PM and HM, even if it also reduces slightly the energy consumption over the whole life cycle because of the energy recovery process. Base-case 5: DER oil transformer The total energy consumption for the whole life cycle of the oil-immersed DER transformer base-case is 15.9 TJ, of which 15.6 TJ (i.e. 1.5 GWh) electricity. In the next graph we can see the contribution of each life cycle phase to each impact. Figure 40 - Distribution of environmental impacts of BC 5 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). Within the production phase, the impacts due to the manufacturing processes are very low (maximum of 2% for eutrophication). However, the extraction and production of raw material significantly contributes to some emissions, such as VOC (18%), POP (38%) or PAHs (53%), as well as to the generation of non-hazardous waste because of the high steel and copper content (48%). Core steel is the main material responsible for POP emissions while mineral oil and aluminium induce high PAHs impacts. XXIX The use phase accounts for 97.5% of the energy consumption over the whole life cycle, 99.7% of the electricity use and 97% of the greenhouse gases emissions. These impacts are almost exclusively due to the electricity losses during the use phase. The distribution phase is negligible for all impacts except for PM for which it accounts for around 7% of the emissions because of the transformer transportation. Finally, the end-of-life accounts for 70% of the hazardous waste generated, 38% of PM emissions to the air, 20% of the eutrophication impacts and 5% of heavy metals emissions. For all other impacts, it has a negligible influence. The incineration of oil is the main reason for the contributions to hazardous waste, PM and HM, even if it also reduces slightly the energy consumption over the whole life cycle because of the energy recovery process. Base-case 6: DER dry transformer The total energy consumption for the whole life cycle of the dry-type DER transformer base-case is 16.9 TJ, of which 16.4 TJ (i.e. 1.56 GWh) electricity. In the next graph we can see the contribution of each life cycle phase to each impact. XXX Figure 41 - Distribution of environmental impacts of BC 6 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). Within the production phase, the manufacturing impacts are very small: the maximum contribution is 2% in HM emissions, because of the sheet metal scrap generated during the manufacturing. The material extraction and production are responsible for the important contribution of this phase to the quantity of landfilled waste (33%) because of the high aluminium and core steel content. Also, core steel highly contributes to the important percentage of this phase in terms of POP emissions (48%) and eutrophication (67%) while aluminium results in high PAHs emissions (71%). Also, the VOC emissions (around 9% contribution of the production phase) are mainly the consequence of the production of ceramics. As expected, the use phase is the main contributor to the following impacts: total energy (97%) and electricity consumption (99.6%), water for processing, greenhouse gases emissions (96.5%) and acidification (97.4%). The smallest contributions occur for eutrophication and PAHs (25% and 29%). The electricity losses are the only reason for these impacts as the contribution of maintenance, spare parts or kilometres over product life are negligible in comparison. XXXI The distribution is negligible for all impacts except for PM for which it accounts for around 8% of the emissions because of the transformer transportation. It also represents 1% of the VOC emissions. The end-of-life is only significant for the hazardous and incinerated waste impact (31%) because of the incineration of epoxy resin and other plastics materials during the end-of-life management. Both incineration and disposal of waste are responsible for the contribution of this phase to PM (20%) and eutrophication impacts (6%). Base-case 7: Separation/isolation transformer The total energy consumption for the whole life cycle of the separation/isolation transformer base-case is 63.1 GJ, of which 53.6 GJ (i.e. 5.1 MWh) electricity. In the next graph we can see the contribution of each life cycle phase to each impact. XXXII Figure 42 - Distribution of environmental impacts of BC 7 per life cycle phase (LOT 2 – Preparatory study, VITO, 2011). Within the production phase, the manufacturing impacts are very small: the maximum contribution is 3% in eutrophication, because of the sheet metal scrap generated during the manufacturing. The material extraction and production are responsible for the important contribution of this phase to the quantity of landfilled waste (91%) and eutrophication potential (79%) because of the aluminium and core steel content. Also, core steel highly contributes to the important percentage of this phase in terms of POP emissions (78%) while PAHs (35%), HM (63%) and acidification (44%) impacts are mainly due to the copper. As expected, the use phase is the main contributor to the following impacts: total energy (86%) and electricity consumption (98.9%), water for processing (99.8%), greenhouse gases emissions (84%) and particulate matter (91%). The smallest contributions occur for eutrophication (16%), POPs emissions (20%) and generation of non-hazardous waste (8%). The electricity losses are the main reason for these impacts. The distribution is negligible for all impacts except for PM for which it accounts for around 2.8% of the emissions because of the transformer transportation. It also represents 1.9% of the VOC emissions. XXXIII The end-of-life is also negligible for all impacts except for eutrophication (2.5%) and PM (1.5%). As only metal components are present in the BOM, no material is incinerated (like resin or oil for the other base-cases). Besides, the disposal percentage is low (assumed to be 1%) which explains the low impacts of this life cycle phase. XXXIV ANNEX 8: European Distribution Transformer Loss standards Table 20 - HD428/HD538 Load Losses for Distribution Transformers RATED POWER OIL-FILLED (HD428) UP TO 24kV No-Load Losses for Distribution Transformers DRY TYPE (HD538) DRY TYPE (HD538) OIL-FILLED (HD428) UP TO 24kV LIST A LIST B LIST C 12kV PRIMARY LIST A’ LIST B’ LIST C’ 12kV PRIMARY W W W W W W W W 50 1100 1350 875 N/A 190 145 125 N/A 100 1750 2150 1475 2000 320 260 210 440 160 2350 3100 2000 2700 460 375 300 610 250 3250 4200 2750 3500 650 530 425 820 400 4600 6000 3850 4900 930 750 610 1150 630 /4% 6500 8400 5400 7300 1300 1030 860 1500 630 /6% 6750 8700 5600 7600 1200 940 800 1370 1000 10500 13000 9500 10000 1700 1400 1100 2000 1600 17000 20000 14000 14000 2600 2200 1700 2800 2500 26500 32000 22000 21000 3800 3200 2500 2200 kVA Table 21 - EN 50464-1 No load losses P (W) and sound power level (Lw ) for U≤24 kV. Rated power kVA E0 D0 C0 B0 Short circuit impedance A0 P0 LwA P0 LwA P0 LwA P0 LwA P0 LwA W dB(A) W dB(A) W dB(A) W dB(A) W dB(A) 50 190 55 145 50 125 47 110 42 90 39 100 320 59 260 54 210 49 180 44 145 41 160 460 62 375 57 300 52 260 47 210 44 250 650 65 530 60 425 55 360 50 300 47 315 770 67 630 61 520 57 440 52 360 49 400 930 68 750 63 610 58 520 53 430 50 500 1 100 69 880 64 720 59 610 54 510 51 630 1 300 70 1 030 65 860 60 730 55 600 52 630 1 200 70 940 65 800 60 680 55 560 52 800 1 400 71 1 150 66 930 61 800 56 650 53 1 000 1 700 73 1 400 68 1 100 63 940 58 770 55 1 250 2 100 74 1 750 69 1 350 64 1150 59 950 56 % 4 XXXV 1 600 2 600 76 2 200 71 1 700 66 1450 61 1 200 58 2 000 3 100 78 2 700 73 2 100 68 1800 63 1 450 60 2 500 3 500 81 3 200 76 2 500 71 2150 66 1 750 63 6 Table 22 - EN 50464-1 Load losses Pk (W) at 75 °C for Um ≤ 24 kV. Rated power Dk Ck Bk Ak Short circuit impedance KVA W W W W % 50 1 350 1 100 875 750 100 2 150 1 750 1 475 1250 160 3 100 2 350 2 000 1 700 250 4 200 3 250 2 750 2 350 315 5 000 3 900 3 250 2800 400 6 000 4 600 3 850 3 250 500 7 200 5 500 4 600 3 900 630 8 400 6 500 5400 4600 630 8 700 6 750 5 600 4 800 800 10 500 8 400 7 000 6 000 1 000 13 000 10 500 9000 7 600 1 250 16 000 13 500 11 000 9 500 1 600 20 000 17 000 14 000 12 000 2 000 26 000 21 000 18 000 15 000 2 500 32 000 26 500 22 000 18 500 4 6 Table 23 - EN 50464-1 Load losses Pk36 (W) at 75 °C for Um = 36 kV. Rated power Ck36 Bk36 Ak36 KVA W W W 50 1 450 1 250 1 050 100 2 350 1 950 1 650 160 3 350 2 550 2 150 250 4 250 3 500 3 000 400 6 200 4 900 4 150 630 8 800 6 500 5500 Short-circuit impedance % 4 or 4,5 XXXVI 800 10 500 8 400 7 000 1 000 13 000 10 500 8 900 1 250 16 000 13 500 11500 1 600 19 200 17 000 14 500 2 000 24 000 21000 18 000 2 500 29 400 26 500 22 500 6 Table 24 - EN 50464-1 No load losses P036 (W) and sound power level (Lw (A) ) for Um = 36 kV. Rated power kVA C036 B036 Short-circuit impedance A036 P0 LwA P0 LwA P0 LwA W dB(A) W dB(A) W dB(A) 50 230 52 190 52 160 50 100 380 56 320 56 270 54 160 520 59 460 59 390 57 250 780 62 650 62 550 60 400 1 120 65 930 65 790 63 630 1 450 67 1 300 67 1 100 65 800 1 700 68 1 500 68 1 300 66 1 000 2000 68 1 700 68 1 450 67 1 250 2 400 70 2 100 70 1 750 68 1 600 2 800 71 2 600 71 2 200 69 2 000 3 400 73 3 150 73 2 700 71 2 500 4 100 76 3 800 76 3 200 73 % 4 or 4,5 6 XXXVII