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Process Data set: Fuel oil heavy at refinery; from crude oil; production mix, at refinery; 1 % mass sulphur content (en) en

Key Data Set Information
Location MY
Geographical representativeness description The data set represents the country specific situation in Malaysia, focusing on the main technologies, the region specific characteristics and / or import statistics.
Reference year 2013
Name
Base name ; Treatment, standards, routes ; Mix and location types ; Quantitative product or process properties
Fuel oil heavy at refinery; from crude oil; production mix, at refinery; 1 % mass sulphur content
Use advice for data set The data set can be used for all LCA/CF studies where the specific refinery product is needed. Combination with individual unit processes using this commodity enables the generation of user-specific (product) LCAs.
Technical purpose of product or process Supply of 1 kg heavy fuel oil (HFO) for power plants and other consumers.
Classification
Class name : Hierarchy level
  • GaBiCategories: Energy carriers / Crude oil based energy carriers
General comment on data set For each material or good with domestic production a regionalized LCI data set was established using Malaysian specific energy supply chains and if possible also Malaysian specific preliminary products. The regionalisation was conducted based on the product systems in the GaBi 6.4 data base. Most of these product systems for materials/goods have German, European or Global boundary conditions. Energy: All energy data sets with exception of the compressed air processes (unit processes) are modelled with Malaysian boundary conditions. Fuel mixes (import and domestic production) are modelled according to statistical data and specific emission data for the relevant production countries and transportation routes. Inorganic and organic chemicals: For all inorganic and organic chemicals the assumption was made that thermal energy and steam is generated from natural gas. Minerals: According to the Malaysian Mineral Yearbook close to 100% of the Gypsum is imported from Thailand and Barite is imported from Thailand and China. These data sets were regionalized with Thai or Chinese energy data sets. Construction materials: The energy carriers used for the production of cement, calcium oxide or particles board varies a lot depending on county and region. For the cement production and lime (calcium oxide) production 95% coal use and 5% use of palm kernel shell (PKS) will be assumed based on several publications. The use of old tyres was neglected. For the production of particle boards or plywood energy supply (power and thermal energy) by biomass was assumed. Metals: The regionalization was done based on the experts at SIRIM and several publications as well as an extended internet research. For the metals gold, zinc, ferro chrome, ferro nickel and primary lead 100% or close to 100% import was found. A real regionalization (production in Malaysia) was not done for these metals, instead an import based on global production and the transport to Malaysia was modelled, resulting in so called consumption mixes. A copper matte process (100% import), a regionalized copper process based on imported copper matte and an additional global copper mix process were generated. Primary aluminium is not produced in Malaysia. The aluminium sheet and profile processes are based on a global primary aluminium mix, the extrusion process and the sheet making processes are regionalized.
Copyright Yes
Owner of data set
Quantitative reference
Reference flow(s)
Time representativeness
Data set valid until 2018
Time representativeness description Annual average
Technological representativeness
Technology description including background system Foreground system: Petroleum refineries are complex plants. The combination and sequence of a large number of processes is usually very specific to the characteristics of the crude oil and the products to be produced. Additional influencing factors are the market demand for the type of products, the available crude oil quality and certain requirements set by authorities the configuration and complexity of a refinery. Simple hydro-skimming refineries can process only a few crude oil qualities and produce few high-quality products. Complex refineries with many conversion plants can process different crude oil types. Petroleum refinery activities start with the reception of crude oil. After desalting, the crude oil is feeded to the distilling column of the atmospheric distillation (fractionation of the crude oil by separation according to density/ boiling/ condensation areas). The light ends (gases) go up to the head of the column and are employed to the liquid gas system to recover methane and ethane for use as refinery fuel and LPG (propane and butane) as saleable products. This light product separation is done in almost every refinery. These gases can also be used in a steam-reforming process to produce hydrogen, which is needed for the desulphurisation processes, the hydro cracking and to a lesser extent for the isomerisation unit. The straight-run naphtha of the atmospheric distillation, which is taken in the upper trays of the column are spitted and fed to three different processes. The light naphtha fraction is introduced to the chemical sweeten process. Some sweeted naphtha is directly blended in the gasoline pool, the main fraction is sent to the isomerisation unit where the aliphatic paraffins are converted into iso-paraffins with a high octane value. Often there is a de-isopentaniser (distillation) downstream to increase the gain of iso-components. These iso-paraffins are very valuable components for the gasoline production with high RON content. After desulphurisation the heavy naphtha fractions are sent to the reformer for catalytic transformation from aliphatic paraffins to iso-paraffins and from cyclo-paraffins to aromatic compounds, with a reduction of the net calorific value. The specific feature of this process is the production of hydrogen (the only hydrogen producer besides additional plants, like steam-reforming). The outputs of the isomerisation (often including a de-isopentaniser) and catalytic reforming go to the gasoline blending system and premium or regular gasoline follow as products. Kerosene is directly obtained from the atmospheric distillation and is separately treated from the rest of the middle distillates fraction. The main part of the middle distillates produced in the atmospheric distillation is employed into the hydrofiner (for desulphurisation). The desulphurised product is fed to the middle distillate blender. The residue from the atmospheric distillation is, mainly, introduced to the vacuum distillation. Here there is a distillation in light vacuum gas oil, vacuum gas oil (wax distillate) and vacuum residue. A part of the atmospheric residue is fed into the visbreaker (mild thermal cracking). Small amounts are introduced directly into the heating oil blending system and the asphalt-blowing process. The light gas oil, as a product of the vacuum distillation, goes to the hydrofiner, is desulphurised, and employed to the middle distillate blender. Some of the vacuum distillate, which has been taken from the middle trays of the vacuum distillation, is introduced to the base oil production of lubricants and waxes. Most of it is fed either to a catalytic cracker (first desulphurised) or a hydrocracker, where the feeds are converted into shorter chains by molecule restructuring. The products are gases, gasoline, middle distillates and heavy cycle gas oils (components of the heavy fuel oil). The gases of the catalytic cracking are treated in an alkylation and polymerisation unit to manufacture additional valuable gasoline components. These processes are used to combine small petroleum molecules into larger ones. Butylene of the catalytic cracker is further used to produce Methyl-Tertiary- Butyl- Ether (MTBE), a product used as octane booster. Sometimes, external purchased bio-ethanol is used instead. The naphtha of the FCC has to be treated in a special desulphurisation process to reduce the high sulphur content. The vacuum residues go into the coking process, which produces gases, gasoline, middle distillates and heating oil. A further product is petroleum coke, which is then purified. The vacuum residue, like some of the atmospheric residue, is also used as feed for the visbreaking, which also produces gases, naphtha, middle distillates and heating oil. The extracted hydrogen sulphides of all desulphurisation processes are fed to a sulphur recovery unit (claus plant) to recover elemental sulphur. The energy generation (heat, steam and electricity) requires a large amount of fuels. The fuel burned in refineries power plants and incinerators may be refinery gas, heating oil (residual oil), petrol coke and sometimes middle distillates and LPG. Beside purchased natural gas and electricity is employed. All important material and energy flows (input- output) are shown in the following graph system boundary of the refinery model. Furthermore a simplified flow chart is shown below. The arrangement of these processes varies among refineries, and few, if any, employ all of these processes. The data set describes a mass-weighted average refinery for the respective country / region. The data set considers the whole supply chain from crude oil exploration / well installation, production, transport to refining operation. If indicated in the process name, some fuels have certain shares of bio-components. The supply of these bio-components (bio-ethanol and bio-diesel) is modelled according to the national / regional situation). Background system: Electricity: Electricity is modelled according to the individual country-specific situations. The country-specific modelling is achieved on multiple levels. Firstly, individual energy carrier specific power plants and plants for renewable energy sources are modelled according to the current national electricity grid mix. Modelling the electricity consumption mix includes transmission / distribution losses and the own use by energy producers (own consumption of power plants and "other" own consumption e.g. due to pumped storage hydro power etc.), as well as imported electricity. Secondly, the national emission and efficiency standards of the power plants are modelled as well as the share of electricity plants and combined heat and power plants (CHP). Thirdly, the country-specific energy carrier supply (share of imports and / or domestic supply) including the country-specific energy carrier properties (e.g. element and energy content) are accounted for. Fourthly, the exploration, mining/production, processing and transport processes of the energy carrier supply chains are modelled according to the specific situation of each electricity producing country. The different production and processing techniques (emissions and efficiencies) in the different energy producing countries are considered, e.g. different crude oil production technologies or different flaring rates at the oil platforms. Thermal energy, process steam: The thermal energy and process steam supply is modelled according to the individual country-specific situation with regard to emission standards and considered energy carriers. The thermal energy and process steam are produced at heat plants. Efficiencies for thermal energy production are by definition 100% in relation to the corresponding energy carrier input. For process steam the efficiency ranges from 85%, 90% to 95%. The energy carriers used for the generation of thermal energy and process steam are modelled according to the specific import situation (see electricity above). Transports: All relevant and known transport processes are included. Ocean-going and inland ship transport as well as rail, truck and pipeline transport of bulk commodities are considered. Energy carriers: The energy carriers are modelled according to the specific supply situation (see electricity above). Refinery products: Diesel fuel, gasoline, technical gases, fuel oils, lubricants and residues such as bitumen are modelled with a parameterised country-specific refinery model. The refinery model represents the current national standard in refining techniques (e.g. emission level, internal energy consumption, etc.) as well as the individual country-specific product output spectrum, which can be quite different from country to country. The supply of crude oil is modelled, again, according to the country-specific situation with the respective properties of the resources.
Pictogram of technology
Flow diagram(s) or picture(s)
  • Energy_Refinery_Flow_chart.jpg Image
  • Energy_Refinery_Output_MY_2010.JPG Image
LCI method and allocation
Type of data set LCI result
LCI Method Principle Attributional
Deviation from LCI method principle / explanations None
LCI method approaches
  • Allocation - mass
  • Allocation - net calorific value
Deviations from LCI method approaches / explanations For all products of the refinery, allocation by mass and net calorific value is applied. The feedstock (crude oil) is allocated by energy, the refinery efforts (emissions) by mass to each product. The production route of every refinery product is modelled in detail, and therefore it is possible to track the energy efforts for operating each single unit processes of the refinery. These energy demand and the corresponding emissions, can be allocated causer-oriented to each refinery product. The feedstock of the respective unit process, which is necessary for the production of a product or an intermediate product, is allocated by energy (i.e. mass of the product * net calorific value of the product). In these way products with high caloric values, e.g. gasoline or gases are assigned to higher feedstock consumption and hence higher environmental upstream impacts compared with low caloric value products (e.g. asphalt, residual oil). The energy demand (thermal energy, steam, electricity) of a process, e.g. atmospheric distillation, being required to create a product or a intermediate product, are allocated according to the share of the throughput of the unit process (mass allocation). In general, products which are more complex to produce and therefore pass a lot of refinery facilities e.g. gasoline, are assigned with a higher energy consumption values (and hence higher emissions) compared with e.g. straight-run products. For the combined crude oil, natural gas and natural gas liquids (NGL) production allocation by net calorific value is applied.
Modelling constants All data used in the calculation of the LCI results refer to net calorific value.
Deviation from modelling constants / explanations None
LCA methodology report
Data sources, treatment and representativeness
Data cut-off and completeness principles Cut-off rules for each unit process: Coverage of at least 95 % of mass and energy of the input and output flows, and 98 % of their environmental relevance (according to expert judgement). For further details please see the document "GaBi Databases Modelling Principles"
Deviation from data cut-off and completeness principles / explanations The coverage of the exploration and well installation data (crude oil, natural gas, natural gas liquids) are only 90% of mass and energy and 95% of the environmental relevance (according to expert judgment).
Data selection and combination principles The data sources for the complete product system are sufficiently consistent: The data on the energy carrier supply chain are based on statistics with country / region-specific transport distances and energy carrier composition, as well as industry and literature data on the inventory of exploration, production and processing. Infrastructure data are from literature. Refinery data are also based on statistical data and measurements of major refineries as well as literature data. LCI modelling is fully consistent.
Deviation from data selection and combination principles / explanations None
Data treatment and extrapolations principles Malaysian conditions for power and thermal energy supply were used based on statistics and technology specific data to represent the specific country conditions. Consumption data (energy and materials) of the production mixes are based on technology specific documents representing a global average or European conditions. For the production of intermediates the same principles were applied.
Deviation from data treatment and extrapolations principles / explanations None
Documentation of data quality management
Data source(s) used for this data set
Percentage supply or production covered 95.0 %
Uncertainty adjustments None
Completeness
Completeness of product model All relevant flows quantified
Supported impact assessment methods
  • Anthropogenic Abiotic Depletion Potential (AADP), TU Berlin
  • CML2001 - Apr. 2013, Terrestric Ecotoxicity Potential (TETP inf.)
  • CML2001 - Apr. 2013, Photochem. Ozone Creation Potential (POCP)
  • CML2001 - Apr. 2013, Ozone Layer Depletion Potential (ODP, steady state)
  • CML2001 - Apr. 2013, Marine Aquatic Ecotoxicity Pot. (MAETP inf.)
  • CML2001 - Apr. 2013, Human Toxicity Potential (HTP inf.)
  • CML2001 - Apr. 2013, Global Warming Potential (GWP 100 years), excl biogenic carbon
  • CML2001 - Apr. 2013, Global Warming Potential (GWP 100 years)
  • CML2001 - Apr. 2013, Freshwater Aquatic Ecotoxicity Pot. (FAETP inf.)
  • CML2001 - Apr. 2013, Eutrophication Potential (EP)
  • CML2001 - Apr. 2013, Acidification Potential (AP)
  • CML2001 - Apr. 2013, Abiotic Depletion (ADP fossil)
  • CML2001 - Apr. 2013, Abiotic Depletion (ADP elements)
  • EDIP 2003, Terrestrial eutrophication
  • EDIP 2003, Stratospheric ozone depletion
  • EDIP 2003, Photochemical ozone formation - impact on vegetation
  • EDIP 2003, Photochemical ozone formation - impact on human health and materials
  • EDIP 2003, Global warming
  • EDIP 2003, Aquatic eutrophication
  • EDIP 2003, Acidification potential
  • I02+ v2.1 - Terrestrial ecotoxicity - Midpoint
  • I02+ v2.1 - Terrestrial acidification/nutrification - Midpoint
  • I02+ v2.1 - Respiratory effects - Midpoint
  • I02+ v2.1 - Photochemical oxidation - Midpoint
  • I02+ v2.1 - Ozone layer depletion - Midpoint
  • I02+ v2.1 - Non-renewable energy - Midpoint
  • I02+ v2.1 - Non-carcinogens - Midpoint
  • I02+ v2.1 - Mineral extraction - Midpoint
  • I02+ v2.1 - Ionizing radiation - Midpoint
  • I02+ v2.1 - Global warming 500yr - Midpoint
  • I02+ v2.1 - Carcinogens - Midpoint
  • I02+ v2.1 - Aquatic eutrophication - Midpoint
  • I02+ v2.1 - Aquatic ecotoxicity - Midpoint
  • I02+ v2.1 - Aquatic acidification - Midpoint
  • Primary energy from renewable resources (net cal. value)
  • Primary energy from non renewable resources (net cal. value)
  • Primary energy demand from ren. and non ren. resources (net cal. value)
  • ReCiPe 1.08 Midpoint (H) - Water depletion
  • ReCiPe 1.08 Midpoint (H) - Terrestrial ecotoxicity
  • ReCiPe 1.08 Midpoint (H) - Terrestrial acidification
  • ReCiPe 1.08 Midpoint (H) - Photochemical oxidant formation
  • ReCiPe 1.08 Midpoint (H) - Particulate matter formation
  • ReCiPe 1.08 Midpoint (H) - Ozone depletion
  • ReCiPe 1.08 Midpoint (H) - Metal depletion
  • ReCiPe 1.08 Midpoint (H) - Marine eutrophication
  • ReCiPe 1.08 Midpoint (H) - Marine ecotoxicity
  • ReCiPe 1.08 Midpoint (H) - Ionising radiation
  • ReCiPe 1.08 Midpoint (H) - Human toxicity
  • ReCiPe 1.08 Midpoint (H) - Freshwater eutrophication
  • ReCiPe 1.08 Midpoint (H) - Freshwater ecotoxicity
  • ReCiPe 1.08 Midpoint (H) - Fossil depletion
  • ReCiPe 1.08 Midpoint (H) - Climate change, incl biogenic carbon
  • ReCiPe 1.08 Midpoint (H) - Climate change, default, excl biogenic carbon
  • TRACI 2.1, Smog Air
  • TRACI 2.1, Resources, Fossil fuels
  • TRACI 2.1, Ozone Depletion Air
  • TRACI 2.1, Human toxicity, non-canc. (recommended)
  • TRACI 2.1, Human toxicity, cancer (recommended)
  • TRACI 2.1, Human Health Particulate Air
  • TRACI 2.1, Global Warming Air, incl. biogenic carbon
  • TRACI 2.1, Global Warming Air, excl. biogenic carbon
  • TRACI 2.1, Eutrophication Water
  • TRACI 2.1, Eutrophication Air
  • TRACI 2.1, Eutrophication
  • TRACI 2.1, Ecotoxicity (recommended)
  • TRACI 2.1, Acidification Water
  • TRACI 2.1, Acidification Air
  • TRACI 2.1, Acidification
  • USEtox, Human toxicity, non-canc. (recommended)
  • USEtox, Human toxicity, cancer (recommended)
  • USEtox, Ecotoxicity (recommended)
  • Total freshwater use
  • Total freshwater consumption (including rainwater)
  • Blue water use
  • Blue water consumption
  • Acidification midpoint (v1.06)
  • Ecotoxicity freshwater midpoint (v1.06)
  • Eutrophication freshwater midpoint (v1.06)
  • Human toxicity midpoint, cancer effects (v1.06)
  • Human toxicity midpoint, non-cancer effects (v1.06)
  • Ionizing radiation midpoint, human health (v1.06)
  • Climate change midpoint, excl biogenic carbon (v1.06)
  • Climate change midpoint, incl biogenic carbon (v1.06)
  • Eutrophication marine midpoint (v1.06)
  • Ozone depletion midpoint (v1.06)
  • Particulate matter/Respiratory inorganics midpoint (v1.06)
  • Photochemical ozone formation midpoint, human health (v1.06)
  • Resource depletion, mineral, fossils and renewables, midpoint (v1.06)
  • Eutrophication terrestrial midpoint (v1.06)
Completeness elementary flows, per topic
  • Noise: No statement
Validation
Type of review Scope / Method(s) of review Data quality indicators
Dependent internal review
Scope name Method name
Unit process(es), black box
  • Energy balance
  • Cross-check with other source
  • Cross-check with other data set
  • Element balance
  • Validation of data sources
  • Expert judgement
  • Mass balance
  • Compliance with ISO 14040 to 14044
  • Sample tests on calculations
Unit process(es), single operation
  • Energy balance
  • Cross-check with other source
  • Cross-check with other data set
  • Element balance
  • Validation of data sources
  • Expert judgement
  • Mass balance
  • Compliance with ISO 14040 to 14044
  • Sample tests on calculations
Documentation
  • Compliance with ISO 14040 to 14044
  • Expert judgement
Life cycle inventory methods
  • Compliance with ISO 14040 to 14044
Raw data
  • Validation of data sources
  • Expert judgement
  • Cross-check with other source
  • Sample tests on calculations
LCIA results
  • Expert judgement
  • Cross-check with other source
  • Cross-check with other data set
LCI results or Partly terminated system
  • Energy balance
  • Cross-check with other source
  • Cross-check with other data set
  • Element balance
  • Validation of data sources
  • Expert judgement
  • Mass balance
  • Compliance with ISO 14040 to 14044
  • Sample tests on calculations
  • Overall quality: Good
  • Methodological appropriateness and consistency: Good
  • Precision: Good
  • Completeness: Good
  • Geographical representativeness: Good
  • Time representativeness: Very good
  • Technological representativeness: Good
Reviewer name and institution
Compliance Declarations
Compliance
Compliance system name
Approval of overall compliance
Fully compliant
Nomenclature compliance
Fully compliant
Methodological compliance
Fully compliant
Review compliance
Fully compliant
Documentation compliance
Fully compliant
Quality compliance
Not defined
Compliance
Compliance system name
Approval of overall compliance
Not defined
Nomenclature compliance
Not defined
Methodological compliance
Not defined
Review compliance
Not defined
Documentation compliance
Not defined
Quality compliance
Not defined
Compliance
Compliance system name
Approval of overall compliance
Not defined
Nomenclature compliance
Fully compliant
Methodological compliance
Fully compliant
Review compliance
Not defined
Documentation compliance
Fully compliant
Quality compliance
Not defined
Commissioner and goal
Commissioner of data set
Intended applications This background data set can be used for the generation of user-specific (product) LCAs.
Data generator
Data set generator / modeller
Data entry by
Time stamp (last saved) 2015-03-01T07:00:00+08:00
Data set format(s)
Data entry by
Official approval of data set by producer/operator
Publication and ownership
UUID 72ab83b9-9fa1-48ae-a5ce-87295ff6979f
Date of last revision 2015-03-01T07:00:00+08:00
Data set version 09.00.000
Workflow and publication status Data set finalised; entirely published
Unchanged re-publication of
Owner of data set
Copyright Yes
License type Other
Access and use restrictions The data set can be used free of charge by anybody to perform LCA studies, to distribute it to third parties, to convert it to other formats, to develop own data sets etc. as long as the copyright and license conditions for the data sets of the Malaysian Life Cycle Inventory Database and the ILCD format are met that can be accessed via http://lca.jrc.ec.europa.eu. Please note e.g. that reference must be given to the 'Owner of data set' and to the 'Malaysian Life Cycle Inventory Database' plus version number, when using the data set or parts thereof. Please note also, that any modifications/omissions of the data set results in invalidity of any existing 'Official approval of data set by producer/operator', that the impression must be avoided that this would still be a complete data set of the Malaysian Life Cycle Inventory Database, and that the content of further fields has to be adjusted. For details see the aforementioned copyright and license conditions.
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