{ "url": "https://openlegislation.uk/eu-directive-2009-30/annex", "json_url": "https://openlegislation.uk/eu-directive-2009-30/annex.json", "legislation": "eudr/2009/30", "legislation_title": "Directive 2009/30/EC of the European Parliament and of the Council of 23 April 2009 amending Directive 98/70/EC as regards the specification of petrol, diesel and gas-oil and introducing a mechanism to monitor and reduce greenhouse gas emissions and amending Council Directive 1999/32/EC as regards the specification of fuel used by inland waterway vessels and repealing Directive 93/12/EEC (Text with EEA relevance)", "legislation_url": "https://openlegislation.uk/eu-directive-2009-30", "path": "annex", "kind": "annex", "number": null, "heading": null, "text": "‘ANNEX I\nENVIRONMENTAL SPECIFICATIONS FOR MARKET FUELS TO BE USED FOR VEHICLES EQUIPPED WITH POSITIVE-IGNITION ENGINES\nType: Petrol\nTest methods shall be those specified in EN 228:2004. Member States may adopt the analytical method specified in replacement EN 228:2004 standard if it can be shown to give at least the same accuracy and at least the same level of precision as the analytical method it replaces.\nThe values quoted in the specification are ‘true values’. In the establishment of their limit values, the terms of EN ISO 4259:2006 ‘Petroleum products — Determination and application of precision data in relation to methods of test’ have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account (R = reproducibility). The results of individual measurements shall be interpreted on the basis of the criteria described in EN ISO 4259:2006.\nMember States may decide to continue to permit the placing on the market of unleaded regular grade petrol with a minimum motor octane number (MON) of 81 and a minimum research octane number (RON) of 91.\nThe summer period shall begin no later than 1 May and shall not end before 30 September. For Member States with low ambient summer temperatures the summer period shall begin no later than 1 June and shall not end before 31 August.\nIn the case of Member States with low ambient summer temperatures and for which a derogation is in effect in accordance with Article 3(4) and (5), the maximum vapour pressure shall be 70 kPa. In the case of Member States for which a derogation is in effect in accordance with Article 3(4) and (5) for petrol containing ethanol, the maximum vapour pressure shall be 60 kPa plus the vapour pressure waiver specified in Annex III.\nOther mono-alcohols and ethers with a final boiling point no higher than that stated in EN 228:2004.\nParameter\nUnit\nLimits\nMinimum\nMaximum\nResearch octane number\n95\n—\nMotor octane number\n85\n—\nVapour pressure, summer period\nkPa\n—\n60,0\nDistillation:\npercentage evaporated at 100 °C\n% v/v\n46,0\n—\npercentage evaporated at 150 °C\n% v/v\n75,0\n—\nHydrocarbon analysis:\nolefins\n% v/v\n—\n18,0\naromatics\n% v/v\n—\n35,0\nbenzene\n% v/v\n—\n1,0\nOxygen content\n% m/m\n3,7\nOxygenates\nMethanol\n% v/v\n3,0\nEthanol (stabilising agents may be necessary)\n% v/v\n10,0\nIso-propyl alcohol\n% v/v\n—\n12,0\nTert-butyl alcohol\n% v/v\n—\n15,0\nIso-butyl alcohol\n% v/v\n—\n15,0\nEthers containing five or more carbon atoms per molecule\n% v/v\n—\n22,0\nOther oxygenates\n% v/v\n—\n15,0\nSulphur content\nmg/kg\n—\n10,0\nLead content\ng/l\n—\n0,005\nANNEX II\nENVIRONMENTAL SPECIFICATIONS FOR MARKET FUELS TO BE USED FOR VEHICLES EQUIPPED WITH COMPRESSION IGNITION ENGINES\nType: Diesel\nTest methods shall be those specified in EN 590:2004. Member States may adopt the analytical method specified in replacement EN 590:2004 standard if it can be shown to give at least the same accuracy and at least the same level of precision as the analytical method it replaces.\nThe values quoted in the specification are ‘true values’. In the establishment of their limit values, the terms of EN ISO 4259:2006 ‘Petroleum products — Determination and application of precision data in relation to methods of test’ have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account (R = reproducibility). The results of individual measurements shall be interpreted on the basis of the criteria described in EN ISO 4259:2006.\nFAME shall comply with EN 14214.\nParameter\nUnit\nLimits\nMinimum\nMaximum\nCetane number\n51,0\n—\nDensity at 15 °C\nkg/m\n—\n845,0\nDistillation:\n95 % v/v recovered at:\n°C\n—\n360,0\nPolycyclic aromatic hydrocarbons\n% m/m\n—\n8,0\nSulphur content\nmg/kg\n—\n10,0\nFAME content — EN 14078\n% v/v\n—\n7,0\nANNEX III\nVAPOUR PRESSURE WAIVER PERMITTED FOR PETROL CONTAINING BIOETHANOL\nBioethanol content (% v/v)\nVapour pressure waiver permitted (kPa)\n0\n0\n1\n3,65\n2\n5,95\n3\n7,20\n4\n7,80\n5\n8,0\n6\n8,0\n7\n7,94\n8\n7,88\n9\n7,82\n10\n7,76\nThe permitted vapour pressure waiver for intermediate bioethanol content between the values listed shall be determined by a straight line interpolation between the bioethanol content immediately above and that immediately below the intermediate value.\nANNEX IV\nRULES FOR CALCULATING LIFE CYCLE GREENHOUSE EMISSIONS FROM BIOFUELS\nA.\nTypical and default values for biofuels if produced with no net carbon emissions from land use change\nNot including animal oil produced from animal by-products classified as category 3 material in accordance with Regulation (EC) No 1774/2002 of the European Parliament and of the Council of 3 October 2002 laying down health rules concerning animal by-products not intended for human consumption.\nOJ L 273, 10.10.2002, p. 1.\nBiofuel production pathway\nTypical greenhouse gas emission saving\nDefault greenhouse gas emission saving\nSugar beet ethanol\n61 %\n52 %\nWheat ethanol (process fuel not specified)\n32 %\n16 %\nWheat ethanol (lignite as process fuel in CHP plant)\n32 %\n16 %\nWheat ethanol (natural gas as process fuel in conventional boiler)\n45 %\n34 %\nWheat ethanol (natural gas as process fuel in CHP plant)\n53 %\n47 %\nWheat ethanol (straw as process fuel in CHP plant)\n69 %\n69 %\nCorn (maize) ethanol, Community produced (natural gas as process fuel in CHP plant)\n56 %\n49 %\nSugar cane ethanol\n71 %\n71 %\nThe part from renewable sources of ethyl-Tertio-butyl-ether (ETBE)\nEqual to that of the ethanol production Pathway used\nThe part from renewable sources of tertiary-amyl-ethyl-ether (TAEE)\nEqual to that of the ethanol production pathway used\nRape seed biodiesel\n45 %\n38 %\nSunflower biodiesel\n58 %\n51 %\nSoybean biodiesel\n40 %\n31 %\nPalm oil biodiesel (process not specified)\n36 %\n19 %\nPalm oil biodiesel (process with methane capture at oil mill)\n62 %\n56 %\nWaste vegetable or animal oil biodiesel\n88 %\n83 %\nHydrotreated vegetable oil from rape seed\n51 %\n47 %\nHydrotreated vegetable oil from sunflower\n65 %\n62 %\nHydrotreated vegetable oil from palm oil (process not specified)\n40 %\n26 %\nHydrotreated vegetable oil from palm oil (process with methane capture at oil mill)\n68 %\n65 %\nPure vegetable oil from rape seed\n58 %\n57 %\nBiogas from municipal organic waste as compressed natural gas\n80 %\n73 %\nBiogas from wet manure as compressed natural gas\n84 %\n81 %\nBiogas from dry manure as compressed natural gas\n86 %\n82 %\nB.\nEstimated typical and default values for future biofuels that were not on the market or were on the market only in negligible quantities in January 2008, if produced with no net carbon emissions from land use change\nBiofuel production pathway\nTypical greenhouse gas emission saving\nDefault greenhouse gas emission saving\nWheat straw ethanol\n87 %\n85 %\nWaste wood ethanol\n80 %\n74 %\nFarmed wood ethanol\n76 %\n70 %\nWaste wood Fischer-Tropsch diesel\n95 %\n95 %\nFarmed wood Fischer-Tropsch diesel\n93 %\n93 %\nWaste wood dimethylether (DME)\n95 %\n95 %\nFarmed wood DME\n92 %\n92 %\nWaste wood methanol\n94 %\n94 %\nFarmed wood methanol\n91 %\n91 %\nThe part from renewable sources of methyl-tertio-butyl-ether (MTBE)\nEqual to that of the methanol production pathway used\nC.\nMethodology\n1.\nGreenhouse gas emissions from the production and use of biofuels shall be calculated as:\nE = eec + el + ep + etd + eu – esca – eccs – eccr – eee\nwhere\nE total emissions from the use of the fuel;\neec emissions from the extraction or cultivation of raw materials;\nel annualised emissions from carbon stock changes caused by land use change;\nep emissions from processing;\netd emissions from transport and distribution;\neu emissions from the fuel in use;\nesca emission savings from soil carbon accumulation via improved agricultural management;\neccs emission savings from carbon capture and geological storage;\neccr emission savings from carbon capture and replacement; and\neee emission savings from excess electricity from cogeneration.\nEmissions from the manufacture of machinery and equipment shall not be taken into account.\n2.\nGreenhouse gas emissions from fuels, E, shall be expressed in terms of grams of CO2 equivalent per MJ of fuel, gCO2eq/MJ.\n3.\nBy derogation from point 2, values calculated in terms of gCO2eq/MJ may be adjusted to take into account differences between fuels in useful work done, expressed in terms of km/MJ. Such adjustments shall only be made where evidence of the differences in useful work done is provided.\n4.\nGreenhouse gas emission savings from biofuels shall be calculated as:\nSAVING = (EF – EB )/EF\nwhere\nEB total emissions from the biofuel; and\nEF total emissions from the fossil fuel comparator.\n5.\nThe greenhouse gases taken into account for the purposes of point 1 shall be CO2, N2O and CH4. For the purpose of calculating CO2 equivalence, those gases shall be valued as follows:\nCO2 1\nN2O 296\nCH4 23\n6.\nEmissions from the extraction or cultivation of raw materials, eec, shall include emissions from the extraction or cultivation process itself; from the collection of raw materials; from waste and leakages; and from the production of chemicals or products used in extraction or cultivation. Capture of CO2 in the cultivation of raw materials shall be excluded. Certified reductions of greenhouse gas emissions from flaring at oil production sites anywhere in the world shall be deducted. Estimates of emissions from cultivation may be derived from the use of averages calculated for smaller geographical areas than those used in the calculation of the default values, as an alternative to using actual values.\n7.\nAnnualised emissions from carbon stock changes caused by land use change, el, shall be calculated by dividing total emissions equally over 20 years. For the calculation of those emissions the following rule shall be applied:\nel = (CSR – CSA ) × 3,664 × 1/20 × 1/P – eB ,\nwhere\nel annualised greenhouse gas emissions from carbon stock change due to land use change (measured as mass of CO2-equivalent per unit biofuel energy);\nCSR the carbon stock per unit area associated with the reference land use (measured as mass of carbon per unit area, including both soil and vegetation). The reference land use shall be the land use in January 2008 or 20 years before the raw material was obtained, whichever was the later;\nCSA the carbon stock per unit area associated with the actual land use (measured as mass of carbon per unit area, including both soil and vegetation). In cases where the carbon stock accumulates over more than one year, the value attributed to CSA shall be the estimated stock per unit area after 20 years or when the crop reaches maturity, whichever is the earlier;\nP the productivity of the crop (measured as biofuel energy per unit area per year); and\neB bonus of 29 gCO2eq/MJ biofuel if biomass is obtained from restored degraded land under the conditions provided for in point 8.\n8.\nThe bonus of 29 gCO2eq/MJ shall be attributed if evidence is provided that the land:\n(a) was not in use for agriculture or any other activity in January 2008; and\n(b) falls into one of the following categories:\n(i) severely degraded land, including such land that was formerly in agricultural use;\n(ii) heavily contaminated land.\nThe bonus of 29 gCO2eq/MJ shall apply for a period of up to 10 years from the date of conversion of the land to agricultural use, provided that a steady increase in carbon stocks as well as a sizable reduction in erosion phenomena for land falling under (i) are ensured and that soil contamination for land falling under (ii) is reduced.\n9.\nThe categories mentioned in point 8(b) are defined as follows:\n(a) ‘severely degraded land’ means land that, for a significant period of time, has either been significantly salinated or presented significantly low organic matter content and been severely eroded;\n(b) ‘heavily contaminated land’ means land that is unfit for the cultivation of food and feed due to soil contamination.\nSuch land shall include land that has been the subject of a Commission decision in accordance with the fourth subparagraph of Article 7c(3).\n10.\nThe guide adopted pursuant to point 10 of Part C of Annex V to Directive 2009/28/EC shall serve as the basis of the calculation of land carbon stocks for the purposes of this Directive.\n11.\nEmissions from processing, ep , shall include emissions from the processing itself; from waste and leakages; and from the production of chemicals or products used in processing.\nIn accounting for the consumption of electricity not produced within the fuel production plant, the greenhouse gas emission intensity of the production and distribution of that electricity shall be assumed to be equal to the average emission intensity of the production and distribution of electricity in a defined region. As an exception to this rule producers may use an average value for an individual electricity production plant for electricity produced by that plant, if that plant is not connected to the electricity grid.\n12.\nEmissions from transport and distribution, etd , shall include emissions from the transport and storage of raw and semi-finished materials and from the storage and distribution of finished materials. Emissions from transport and distribution to be taken into account under point 6 shall not be covered by this point.\n13.\nEmissions from the fuel in use, eu , shall be taken to be zero for biofuels.\n14.\nEmission savings from carbon capture and geological storage eccs , that have not already been accounted for in ep , shall be limited to emissions avoided through the capture and sequestration of emitted CO2 directly related to the extraction, transport, processing and distribution of fuel.\n15.\nEmission savings from carbon capture and replacement, eccr , shall be limited to emissions avoided through the capture of CO2 of which the carbon originates from biomass and which is used to replace fossil-derived CO2 used in commercial products and services.\n16.\nEmission savings from excess electricity from cogeneration, eee , shall be taken into account in relation to the excess electricity produced by fuel production systems that use cogeneration except where the fuel used for the cogeneration is a co-product other than an agricultural crop residue. In accounting for that excess electricity, the size of the cogeneration unit shall be assumed to be the minimum necessary for the cogeneration unit to supply the heat that is needed to produce the fuel. The greenhouse gas emission savings associated with that excess electricity shall be taken to be equal to the amount of greenhouse gas that would be emitted when an equal amount of electricity was generated in a power plant using the same fuel as the cogeneration unit.\n17.\nWhere a fuel production process produces, in combination, the fuel for which emissions are being calculated and one or more other products (co-products), greenhouse gas emissions shall be divided between the fuel or its intermediate product and the co-products in proportion to their energy content (determined by lower heating value in the case of co-products other than electricity).\n18.\nFor the purposes of the calculation referred to in point 17, the emissions to be divided shall be eec + el + those fractions of ep , etd and eee that take place up to and including the process step at which a co-product is produced. If any allocation to co-products has taken place at an earlier process step in the life-cycle, the fraction of those emissions assigned in the last such process step to the intermediate fuel product shall be used for this purpose instead of the total of those emissions.\nAll co-products, including electricity that does not fall under the scope of point 16, shall be taken into account for the purposes of that calculation, except for agricultural crop residues, including straw, bagasse, husks, cobs and nut shells. Co-products that have a negative energy content shall be considered to have an energy content of zero for the purpose of the calculation.\nWastes, agricultural crop residues, including straw, bagasse, husks, cobs and nut shells, and residues from processing, including crude glycerine (glycerine that is not refined), shall be considered to have zero life-cycle greenhouse gas emissions up to the process of collection of those materials.\nIn the case of fuels produced in refineries, the unit of analysis for the purposes of the calculation referred to in point 17 shall be the refinery.\n19.\nFor the purposes of the calculation referred to in point 4, the fossil fuel comparator EF shall be the latest available actual average emissions from the fossil part of petrol and diesel consumed in the Community as reported under this Directive. If no such data are available, the value used shall be 83,8 gCO2eq/MJ.\nD.\nDisaggregated default values for biofuels\nDisaggregated default values for cultivation: ‘eec’ as defined in Part C of this Annex\nNot including animal oil produced from animal by-products classified as category 3 material in accordance with Regulation (EC) No 1774/2002.\nBiofuel production pathway\nTypical greenhouse gas emissions(gCO2eq/MJ)\nDefault greenhouse gas emissions(gCO2eq/MJ)\nSugar beet ethanol\n12\n12\nWheat ethanol\n23\n23\nCorn (maize) ethanol, Community produced\n20\n20\nSugar cane ethanol\n14\n14\nThe part from renewable sources of ETBE\nEqual to that of the ethanol production pathway used\nThe part from renewable sources of TAEE\nEqual to that of the ethanol production pathway used\nRape seed biodiesel\n29\n29\nSunflower biodiesel\n18\n18\nSoybean biodiesel\n19\n19\nPalm oil biodiesel\n14\n14\nWaste vegetable or animal oil biodiesel\n0\n0\nHydrotreated vegetable oil from rape seed\n30\n30\nHydrotreated vegetable oil from sunflower\n18\n18\nHydrotreated vegetable oil from palm oil\n15\n15\nPure vegetable oil from rape seed\n30\n30\nBiogas from municipal organic waste as compressed natural gas\n0\n0\nBiogas from wet manure as compressed natural gas\n0\n0\nBiogas from dry manure as compressed natural gas\n0\n0\nDisaggregated default values for processing (including excess electricity): ‘ep – eee’ as defined in Part C of this Annex\nBiofuel production pathway\nTypical greenhouse gas emissions(gCO2eq/MJ)\nDefault greenhouse gas emissions(gCO2eq/MJ)\nSugar beet ethanol\n19\n26\nWheat ethanol (process fuel not specified)\n32\n45\nWheat ethanol (lignite as process fuel in CHP plant)\n32\n45\nWheat ethanol (natural gas as process fuel in conventional boiler)\n21\n30\nWheat ethanol (natural gas as process fuel in CHP plant)\n14\n19\nWheat ethanol (straw as process fuel in CHP plant)\n1\n1\nCorn (maize) ethanol, Community produced (natural gas as process fuel in CHP plant)\n15\n21\nSugar cane ethanol\n1\n1\nThe part from renewable sources of ETBE\nEqual to that of the ethanol production pathway used\nThe part from renewable sources of TAEE\nEqual to that of the ethanol production pathway used\nRape seed biodiesel\n16\n22\nSunflower biodiesel\n16\n22\nSoybean biodiesel\n18\n26\nPalm oil biodiesel (process not specified)\n35\n49\nPalm oil biodiesel (process with methane capture at oil mill)\n13\n18\nWaste vegetable or animal oil biodiesel\n9\n13\nHydrotreated vegetable oil from rape seed\n10\n13\nHydrotreated vegetable oil from sunflower\n10\n13\nHydrotreated vegetable oil from palm oil (process not specified)\n30\n42\nHydrotreated vegetable oil from palm oil (process with methane capture at oil mill)\n7\n9\nPure vegetable oil from rape seed\n4\n5\nBiogas from municipal organic waste as compressed natural gas\n14\n20\nBiogas from wet manure as compressed natural gas\n8\n11\nBiogas from dry manure as compressed natural gas\n8\n11\nDisaggregated default values for transport and distribution: ‘etd’ as defined in Part C of this Annex\nBiofuel production pathway\nTypical greenhouse gas emissions(gCO2eq/MJ)\nDefault greenhouse gas emissions(gCO2eq/MJ)\nSugar beet ethanol\n2\n2\nWheat ethanol\n2\n2\nCorn (maize) ethanol, Community produced\n2\n2\nSugar cane ethanol\n9\n9\nThe part from renewable sources of ETBE\nEqual to that of the ethanol production pathway used\nThe part from renewable sources of TAEE\nEqual to that of the ethanol production pathway used\nRape seed biodiesel\n1\n1\nSunflower biodiesel\n1\n1\nSoybean biodiesel\n13\n13\nPalm oil biodiesel\n5\n5\nWaste vegetable or animal oil biodiesel\n1\n1\nHydrotreated vegetable oil from rape seed\n1\n1\nHydrotreated vegetable oil from sunflower\n1\n1\nHydrotreated vegetable oil from palm oil\n5\n5\nPure vegetable oil from rape seed\n1\n1\nBiogas from municipal organic waste as compressed natural gas\n3\n3\nBiogas from wet manure as compressed natural gas\n5\n5\nBiogas from dry manure as compressed natural gas\n4\n4\nTotal for cultivation, processing, transport and distribution\nBiofuel production pathway\nTypical greenhouse gas emissions(gCO2eq/MJ)\nDefault greenhouse gas emissions(gCO2eq/MJ)\nSugar beet ethanol\n33\n40\nWheat ethanol (process fuel not specified)\n57\n70\nWheat ethanol (lignite as process fuel in CHP plant)\n57\n70\nWheat ethanol (natural gas as process fuel in conventional boiler)\n46\n55\nWheat ethanol (natural gas as process fuel in CHP plant)\n39\n44\nWheat ethanol (straw as process fuel in CHP plant)\n26\n26\nCorn (maize) ethanol, Community produced (natural gas as process fuel in CHP plant)\n37\n43\nSugar cane ethanol\n24\n24\nThe part from renewable sources of ETBE\nEqual to that of the ethanol production pathway used\nThe part from renewable sources of TAEE\nEqual to that of the ethanol production pathway used\nRape seed biodiesel\n46\n52\nSunflower biodiesel\n35\n41\nSoybean biodiesel\n50\n58\nPalm oil biodiesel (process not specified)\n54\n68\nPalm oil biodiesel (process with methane capture at oil mill)\n32\n37\nWaste vegetable or animal oil biodiesel\n10\n14\nHydrotreated vegetable oil from rape seed\n41\n44\nHydrotreated vegetable oil from sunflower\n29\n32\nHydrotreated vegetable oil from palm oil (process not specified)\n50\n62\nHydrotreated vegetable oil from palm oil (process with methane capture at oil mill)\n27\n29\nPure vegetable oil from rape seed\n35\n36\nBiogas from municipal organic waste as compressed natural gas\n17\n23\nBiogas from wet manure as compressed natural gas\n13\n16\nBiogas from dry manure as compressed natural gas\n12\n15\nE.\nEstimated disaggregated default values for future biofuels that were not on the market or were only on the market in negligible quantities in January 2008\nDisaggregated values for cultivation: ‘eec’ as defined in Part C of this Annex\nBiofuel production pathway\nTypical greenhouse gas missions(gCO2eq/MJ)\nDefault greenhouse gas emissions(gCO2eq/MJ)\nWheat straw ethanol\n3\n3\nWaste wood ethanol\n1\n1\nFarmed wood ethanol\n6\n6\nWaste wood Fischer-Tropsch diesel\n1\n1\nFarmed wood Fischer-Tropsch diesel\n4\n4\nWaste wood DME\n1\n1\nFarmed wood DME\n5\n5\nWaste wood methanol\n1\n1\nFarmed wood methanol\n5\n5\nThe part from renewable sources of MTBE\nEqual to that of the methanol production pathway used\nDisaggregated values for processing (including excess electricity): ‘ep – eee’ as defined in Part C of this Annex\nBiofuel production pathway\nTypical greenhouse gas emissions(gCO2eq/MJ)\nDefault greenhouse gas emissions(gCO2eq/MJ)\nWheat straw ethanol\n5\n7\nWood ethanol\n12\n17\nWood Fischer-Tropsch diesel\n0\n0\nWood DME\n0\n0\nWood methanol\n0\n0\nThe part from renewable sources of MTBE\nEqual to that of the methanol production pathway used\nDisaggregated values for transport and distribution: ‘etd’ as defined in Part C of this Annex\nBiofuel production pathway\nTypical greenhouse gas emissions(gCO2eq/MJ)\nDefault greenhouse gas emissions(gCO2eq/MJ)\nWheat straw ethanol\n2\n2\nWaste wood ethanol\n4\n4\nFarmed wood ethanol\n2\n2\nWaste wood Fischer-Tropsch diesel\n3\n3\nFarmed wood Fischer-Tropsch diesel\n2\n2\nWaste wood DME\n4\n4\nFarmed wood DME\n2\n2\nWaste wood methanol\n4\n4\nFarmed wood methanol\n2\n2\nThe part from renewable sources of MTBE\nEqual to that of the methanol production pathway used\nTotal for cultivation, processing, transport and distribution\nBiofuel production pathway\nTypical greenhouse gas emissions(gCO2eq/MJ)\nDefault greenhouse gas emissions(gCO2eq/MJ)\nWheat straw ethanol\n11\n13\nWaste wood ethanol\n17\n22\nFarmed wood ethanol\n20\n25\nWaste wood Fischer-Tropsch diesel\n4\n4\nFarmed wood Fischer-Tropsch diesel\n6\n6\nWaste wood DME\n5\n5\nFarmed wood DME\n7\n7\nWaste wood methanol\n5\n5\nFarmed wood methanol\n7\n7\nThe part from renewable sources of MTBE\nEqual to that of the methanol production pathway used\n’", "extent": "E+W+S+N.I.", "status": null, "version": "current", "annotations": [ { "type": "footnote", "label": "f1", "text": "Test methods shall be those specified in EN 228:2004. Member States may adopt the analytical method specified in replacement EN 228:2004 standard if it can be shown to give at least the same accuracy and at least the same level of precision as the analytical method it replaces." }, { "type": "footnote", "label": "f2", "text": "The values quoted in the specification are ‘true values’. In the establishment of their limit values, the terms of EN ISO 4259:2006 ‘Petroleum products — Determination and application of precision data in relation to methods of test’ have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account (R = reproducibility). The results of individual measurements shall be interpreted on the basis of the criteria described in EN ISO 4259:2006." }, { "type": "footnote", "label": "f3", "text": "Member States may decide to continue to permit the placing on the market of unleaded regular grade petrol with a minimum motor octane number (MON) of 81 and a minimum research octane number (RON) of 91." }, { "type": "footnote", "label": "f4", "text": "The summer period shall begin no later than 1 May and shall not end before 30 September. For Member States with low ambient summer temperatures the summer period shall begin no later than 1 June and shall not end before 31 August." }, { "type": "footnote", "label": "f5", "text": "In the case of Member States with low ambient summer temperatures and for which a derogation is in effect in accordance with Article 3(4) and (5), the maximum vapour pressure shall be 70 kPa. In the case of Member States for which a derogation is in effect in accordance with Article 3(4) and (5) for petrol containing ethanol, the maximum vapour pressure shall be 60 kPa plus the vapour pressure waiver specified in Annex III." }, { "type": "footnote", "label": "f6", "text": "Other mono-alcohols and ethers with a final boiling point no higher than that stated in EN 228:2004." }, { "type": "footnote", "label": "f7", "text": "Test methods shall be those specified in EN 590:2004. Member States may adopt the analytical method specified in replacement EN 590:2004 standard if it can be shown to give at least the same accuracy and at least the same level of precision as the analytical method it replaces." }, { "type": "footnote", "label": "f8", "text": "The values quoted in the specification are ‘true values’. In the establishment of their limit values, the terms of EN ISO 4259:2006 ‘Petroleum products — Determination and application of precision data in relation to methods of test’ have been applied and in fixing a minimum value, a minimum difference of 2R above zero has been taken into account (R = reproducibility). The results of individual measurements shall be interpreted on the basis of the criteria described in EN ISO 4259:2006." }, { "type": "footnote", "label": "f9", "text": "FAME shall comply with EN 14214." }, { "type": "footnote", "label": "f10", "text": "OJ L 273, 10.10.2002, p. 1." }, { "type": "footnote", "label": "f11", "text": "Not including animal oil produced from animal by-products classified as category 3 material in accordance with Regulation (EC) No 1774/2002 of the European Parliament and of the Council of 3 October 2002 laying down health rules concerning animal by-products not intended for human consumption." }, { "type": "footnote", "label": "f12", "text": "The quotient obtained by dividing the molecular weight of CO2 (44,010 g/mol) by the molecular weight of carbon (12,011 g/mol) is equal to 3,664." }, { "type": "footnote", "label": "f13", "text": "Not including animal oil produced from animal by-products classified as category 3 material in accordance with Regulation (EC) No 1774/2002." } ], "outstanding_effects": [], "provenance": { "source": "legislation.gov.uk", "source_url": "https://www.legislation.gov.uk/eudr/2009/30/annex", "retrieved_at": "2026-11-01T15:22:14.050803+00:00" }, "licence": "Open Government Licence v3.0", "licence_url": "https://www.nationalarchives.gov.uk/doc/open-government-licence/version/3/", "attribution": "Contains public sector information licensed under the Open Government Licence v3.0. Source: legislation.gov.uk, The National Archives." }