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<processDataSet xmlns="http://lca.jrc.it/ILCD/Process" xmlns:common="http://lca.jrc.it/ILCD/Common" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://lca.jrc.it/ILCD/Process ../../schemas/ILCD_ProcessDataSet.xsd" locations="../ILCDLocations.xml" version="1.1">
  <processInformation>
    <dataSetInformation>
      <common:UUID>864a6be9-1a0a-44fb-860a-199bdb66dd60</common:UUID>
      <name>
        <baseName xml:lang="en">Acrylonitrile butadiene styrene (ABS)</baseName>
        <treatmentStandardsRoutes xml:lang="en">emulsion polymerisation, bulk polymerisation or combined processes</treatmentStandardsRoutes>
        <mixAndLocationTypes xml:lang="en">production mix, at producer</mixAndLocationTypes>
        <functionalUnitFlowProperties xml:lang="en">n/a</functionalUnitFlowProperties>
      </name>
      <classificationInformation>
        <common:classification name="GaBiCategories" classes="../GaBiCategories.xml">
          <common:class level="0" classId="61d01af3-23cc-49cc-849f-63a9801953ff">Processes</common:class>
          <common:class level="1" classId="d9e81c75-315c-4c0f-b5d3-e1f5f03d1263">Production</common:class>
          <common:class level="2" classId="455ffb41-4777-4723-954a-492e09d7e56a">Material production</common:class>
          <common:class level="3" classId="cf667b61-9654-473c-993d-16c14c5c2693">Plastic production</common:class>
        </common:classification>
      </classificationInformation>
      <common:generalComment xml:lang="en">The main data source was a data collection from European producers of Acrylonitrile Butadiene Styrene (ABS). Primary data on gate-to-gate ABS production is derived from site-specific information for processes under operational control supplied by the participating companies of this eco-profile.
Primary production data for ABS production are from four different European suppliers: overall five sites for ABS production are included in the average calculations.
This covers more than 90 % of the European ABS (EU-27) production in 2013.</common:generalComment>
    </dataSetInformation>
    <quantitativeReference type="Reference flow(s)">
      <referenceToReferenceFlow>80</referenceToReferenceFlow>
    </quantitativeReference>
    <time>
      <common:referenceYear>2010</common:referenceYear>
      <common:dataSetValidUntil>2022</common:dataSetValidUntil>
      <common:timeRepresentativenessDescription xml:lang="en">The LCI data for ABS production was collected as 12 month averages representing the year 2013. Background data have reference year of 2010 to 2013. Even if all data were related to 2013, major changes in the result are not expected, as technological breakthrough is not known for refining, steam cracking or re-refining technology or one of the related up-stream technologies. These are rather established and if possible constantly optimised technologies. The dataset is considered to be valid until substantial technological changes in the production chain occur.</common:timeRepresentativenessDescription>
    </time>
    <geography>
      <locationOfOperationSupplyOrProduction location="EU-27">
        <descriptionOfRestrictions xml:lang="en">Primary production data for  ABS production are from four different European suppliers each, in five European countries (Belgium, Germany, Italy, Spain and The Netherlands). Fuel and energy inputs in the system reflect average European conditions and whenever applicable, site specific conditions were applied, to reflect representative situations.</descriptionOfRestrictions>
      </locationOfOperationSupplyOrProduction>
    </geography>
    <technology>
      <technologyDescriptionAndIncludedProcesses xml:lang="en">Foreground system:
Acrylonitrile Butadiene Styrene (ABS) can be produced by emulsion polymerisation, bulk polymerisation or combined processes. In the first, ABS graft rubber and SAN (Styrene Acrylonitrile) matrix are either polymerised separately then compounded, or polymerised together. The second starts with butadiene rubber in solvent, followed by a pre-polymerisation of the rubber-monomers mixture under continuous mixing. The polymerisation is finally completed; the product is centrifuged, dried and compounded.

For ABS sold to the market, additives such as lubricants, antioxidants or light stabilisers can also be added.


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.</technologyDescriptionAndIncludedProcesses>
      <technologicalApplicability xml:lang="en">Due to its combination of strength and impact resistance, ABS is widely used as an engineering material. The main consumers are the automotive industry, the domestic appliances industry, the data technology and telecommunications area, and producers of refrigeration equipment, toys, sports articles, and semi-finished articles. 

ABS can be recycled, used articles can be ground and directly recycled in the pro-duction process. Furthermore, energy recovery by incineration is also possible.</technologicalApplicability>
      <referenceToTechnologyFlowDiagrammOrPicture refObjectId="a64cc52d-ca7b-4e96-bbab-3fbb8e9eedcb" version="27.00.000" type="source data set" uri="../sources/a64cc52d-ca7b-4e96-bbab-3fbb8e9eedcb.xml">
        <common:shortDescription xml:lang="en">Plastics_Acrylonitrile butadiene styrene, ABS (PlasticsEurope).jpg</common:shortDescription>
      </referenceToTechnologyFlowDiagrammOrPicture>
    </technology>
    <mathematicalRelations>
      <modelDescription xml:lang="en">The calculation follows the vertical calculation methodology, i.e. that the averaging is done after modelling the specific processes. Restrictions on competition and confidentiality do not allow displaying and describing the systems and analysing details.</modelDescription>
    </mathematicalRelations>
  </processInformation>
  <modellingAndValidation>
    <LCIMethodAndAllocation>
      <typeOfDataSet>LCI result</typeOfDataSet>
      <LCIMethodPrinciple>Attributional</LCIMethodPrinciple>
      <deviationsFromLCIMethodPrinciple xml:lang="en">None</deviationsFromLCIMethodPrinciple>
      <LCIMethodApproaches>Allocation - market value</LCIMethodApproaches>
      <LCIMethodApproaches>Allocation - net calorific value</LCIMethodApproaches>
      <LCIMethodApproaches>Allocation - exergetic content</LCIMethodApproaches>
      <LCIMethodApproaches>Allocation - mass</LCIMethodApproaches>
      <LCIMethodApproaches>Not applicable</LCIMethodApproaches>
      <deviationsFromLCIMethodApproaches>Foreground system:
In some companies information, output material with deviations from the required specification is re-ported. If these materials show only slight differences and are sold at comparable price-level, they are assumed as product output (&lt; 4% of total production); in case of material declared as off-grade sent to recovery, neither further environmental burden nor credits are given to the modelled system (&lt; 1% of total production).
No post-consumer waste is reported as input to the system, therefore no allocation between different life cycles is necessary.

Background system:
In the refinery operations, co-production is addressed by applying allocation based on mass and net calorific value. The chosen allocation in downstream petrochemicals is based on several sensitivity analyses, which were reviewed by petrochemical experts.  Materials and chemicals needed are modelled using the allocation rule most suitable for the respective product (mass, energy, exergy, economic). For further information on specific product see documentation.gabi-software.com.</deviationsFromLCIMethodApproaches>
      <modellingConstants xml:lang="en">All data used in the calculation of the LCI results refer to net calorific value.</modellingConstants>
      <deviationsFromModellingConstants xml:lang="en">None</deviationsFromModellingConstants>
      <referenceToLCAMethodDetails refObjectId="f2b512cd-43b2-4260-9882-eebc06731274" version="27.00.000" type="source data set" uri="../sources/f2b512cd-43b2-4260-9882-eebc06731274.xml">
        <common:shortDescription xml:lang="en">GaBi Modelling Principles</common:shortDescription>
      </referenceToLCAMethodDetails>
      <referenceToLCAMethodDetails refObjectId="1f39e45a-4c3d-4067-a1a9-a11db942c605" version="27.00.000" type="source data set" uri="../sources/1f39e45a-4c3d-4067-a1a9-a11db942c605.xml">
        <common:shortDescription xml:lang="en">Eco-profiles and Environmental Declarations, Version 2.0 (April 2011)</common:shortDescription>
      </referenceToLCAMethodDetails>
    </LCIMethodAndAllocation>
    <dataSourcesTreatmentAndRepresentativeness>
      <dataCutOffAndCompletenessPrinciples xml:lang="en">In the foreground processes all relevant flows are considered, trying to avoid any cut-off of material and energy flows. In single cases additives used in the ABS foreground unit process (&lt;0.3% m/m of product output) are neglected. In such cases, it is assured that no hazardous sub-stances or metals are present in this neglected part. According to the GaBi database used in the background processes, at least 95% of mass and energy of the input and output flows are covered and 98% of their environmental relevance (according to expert judgment) are considered, hence an influence of cut-offs less than 1% on the total is expected. Transports for the main input materials (styrene, alpha-methyl styrene, acrylonitrile) contribute less than 3% to the overall environmental burden. The contribution of transport of small material proportions is expected to be less than 1%; hence the transports for minor input amounts are excluded.</dataCutOffAndCompletenessPrinciples>
      <deviationsFromCutOffAndCompletenessPrinciples xml:lang="en">None</deviationsFromCutOffAndCompletenessPrinciples>
      <dataSelectionAndCombinationPrinciples xml:lang="en">90% coverage of the European industry</dataSelectionAndCombinationPrinciples>
      <deviationsFromSelectionAndCombinationPrinciples xml:lang="en">None</deviationsFromSelectionAndCombinationPrinciples>
      <dataTreatmentAndExtrapolationsPrinciples xml:lang="en">The data set represents the specific situation in Europe, focusing on the main technologies used for producing ABS in Europe. 

Primary production data for ABS production are from four different European suppliers each, in five European countries (Belgium, Germany, Italy, Spain and The Netherlands).</dataTreatmentAndExtrapolationsPrinciples>
      <deviationsFromTreatmentAndExtrapolationPrinciples xml:lang="en">None</deviationsFromTreatmentAndExtrapolationPrinciples>
      <referenceToDataSource refObjectId="61875b4e-7249-444b-8691-e4a04e6d3c47" version="27.00.000" type="source data set" uri="../sources/61875b4e-7249-444b-8691-e4a04e6d3c47.xml">
        <common:shortDescription xml:lang="en">GaBi databases</common:shortDescription>
      </referenceToDataSource>
      <referenceToDataSource refObjectId="5349b289-9209-11dc-8314-0800200c9a66" version="27.00.000" type="source data set" uri="../sources/5349b289-9209-11dc-8314-0800200c9a66.xml">
        <common:shortDescription xml:lang="en">Individual industry data</common:shortDescription>
      </referenceToDataSource>
      <referenceToDataSource refObjectId="25f58de2-5ed7-4f99-a0ee-a8fa2564b28a" version="27.00.000" type="source data set" uri="../sources/25f58de2-5ed7-4f99-a0ee-a8fa2564b28a.xml">
        <common:shortDescription xml:lang="en">Industry sources(confidential data), 2011</common:shortDescription>
      </referenceToDataSource>
      <percentageSupplyOrProductionCovered>90.0</percentageSupplyOrProductionCovered>
      <annualSupplyOrProductionVolume xml:lang="en">The considered participants covered 90% of all ABS production in Europe in 2013.</annualSupplyOrProductionVolume>
      <samplingProcedure xml:lang="en">European producers act as a main source of data for the production of ABS on the basis of a direct questionnaire. Primary data on gate-to-gate ABS production is derived from site specific information for processes under operational control supplied by the participating companies of this study. The data for the upstream supply chain until the precursors are taken from the database of the software system GaBi 6.</samplingProcedure>
      <dataCollectionPeriod xml:lang="en">2013</dataCollectionPeriod>
      <uncertaintyAdjustments xml:lang="en">None</uncertaintyAdjustments>
      <useAdviceForDataSet xml:lang="en">The data set can be used for all LCA/CF studies where the product is needed. Combination with individual unit processes using this commodity enables the generation of user-specific (product) LCAs.

Due to its combination of strength and impact resistance, ABS is widely used as an engineering material. The main consumers are the automotive industry, the domestic appliances industry, the data technology and telecommunications area, and producers of refrigeration equipment, toys, sports articles, and semi-finished articles. 

ABS can be recycled, used articles can be ground and directly recycled in the pro-duction process. Furthermore, energy recovery by incineration is also possible.</useAdviceForDataSet>
    </dataSourcesTreatmentAndRepresentativeness>
    <completeness>
      <completenessProductModel>All relevant flows quantified</completenessProductModel>
      <referenceToSupportedImpactAssessmentMethods refObjectId="01225272-a6e3-44c6-b7c0-7dee880e3f0d" version="27.00.000" type="LCIA method data set">
        <common:shortDescription xml:lang="en">CML2001 - Apr. 2013, Abiotic Depletion (ADP elements)</common:shortDescription>
      </referenceToSupportedImpactAssessmentMethods>
      <referenceToSupportedImpactAssessmentMethods refObjectId="a1b1da7e-f55c-4f83-86b5-8406644c4187" version="27.00.000" type="LCIA method data set">
        <common:shortDescription xml:lang="en">CML2001 - Apr. 2013, Abiotic Depletion (ADP fossil)</common:shortDescription>
      </referenceToSupportedImpactAssessmentMethods>
      <referenceToSupportedImpactAssessmentMethods refObjectId="8831d43f-cb1f-46fa-bdea-192a563e41f6" version="27.00.000" type="LCIA method data set">
        <common:shortDescription xml:lang="en">CML2001 - Apr. 2013, Acidification Potential (AP)</common:shortDescription>
      </referenceToSupportedImpactAssessmentMethods>
      <referenceToSupportedImpactAssessmentMethods refObjectId="b7cc6c77-d43e-4356-b48c-2704b41159be" version="27.00.000" type="LCIA method data set">
        <common:shortDescription xml:lang="en">CML2001 - Apr. 2013, Eutrophication Potential (EP)</common:shortDescription>
      </referenceToSupportedImpactAssessmentMethods>
      <referenceToSupportedImpactAssessmentMethods refObjectId="97b83982-903d-431c-aa4f-7e05aad400e6" version="27.00.000" type="LCIA method data set">
        <common:shortDescription xml:lang="en">CML2001 - Apr. 2013, Global Warming Potential (GWP 100 years)</common:shortDescription>
      </referenceToSupportedImpactAssessmentMethods>
      <referenceToSupportedImpactAssessmentMethods refObjectId="ee41c86c-7cdc-4e0d-9b5e-1c2b598f9a1c" version="27.00.000" type="LCIA method data set">
        <common:shortDescription xml:lang="en">CML2001 - Apr. 2013, Ozone Layer Depletion Potential (ODP, steady state)</common:shortDescription>
      </referenceToSupportedImpactAssessmentMethods>
      <referenceToSupportedImpactAssessmentMethods refObjectId="27e624d1-46ae-4c68-958b-dbeed16b05a2" version="27.00.000" type="LCIA method data set">
        <common:shortDescription xml:lang="en">CML2001 - Apr. 2013, Photochem. Ozone Creation Potential (POCP)</common:shortDescription>
      </referenceToSupportedImpactAssessmentMethods>
      <referenceToSupportedImpactAssessmentMethods refObjectId="804f172d-5d3a-4950-81d7-879f89881a6d" version="27.00.000" type="LCIA method data set">
        <common:shortDescription xml:lang="en">Primary energy demand from ren. and non ren. resources (gross cal. value)</common:shortDescription>
      </referenceToSupportedImpactAssessmentMethods>
      <completenessElementaryFlows type="Noise" value="No statement"/>
    </completeness>
    <validation>
      <review type="Independent external review">
        <common:scope name="Unit process(es), single operation">
          <common:method name="Cross-check with other data set"/>
        </common:scope>
        <common:scope name="Unit process(es), black box">
          <common:method name="Cross-check with other data set"/>
          <common:method name="Expert judgement"/>
        </common:scope>
        <common:scope name="LCI results or Partly terminated system">
          <common:method name="Energy balance"/>
          <common:method name="Expert judgement"/>
          <common:method name="Mass balance"/>
          <common:method name="Documentation"/>
        </common:scope>
        <common:scope name="LCIA results">
          <common:method name="Cross-check with other source"/>
          <common:method name="Expert judgement"/>
        </common:scope>
        <common:scope name="Documentation">
          <common:method name="Cross-check with other source"/>
          <common:method name="Compliance with ISO 14040 to 14044"/>
        </common:scope>
        <common:scope name="Life cycle inventory methods">
          <common:method name="Cross-check with other source"/>
          <common:method name="Compliance with ISO 14040 to 14044"/>
        </common:scope>
        <common:scope name="LCIA results calculation">
          <common:method name="Expert judgement"/>
          <common:method name="Compliance with ISO 14040 to 14044"/>
        </common:scope>
        <common:scope name="Goal and scope definition">
          <common:method name="Cross-check with other source"/>
          <common:method name="Compliance with ISO 14040 to 14044"/>
        </common:scope>
        <dataQualityIndicators xmlns="http://lca.jrc.it/ILCD/Common">
          <dataQualityIndicator name="Technological representativeness" value="Very good"/>
          <dataQualityIndicator name="Time representativeness" value="Good"/>
          <dataQualityIndicator name="Geographical representativeness" value="Good"/>
          <dataQualityIndicator name="Completeness" value="Good"/>
          <dataQualityIndicator name="Precision" value="Very good"/>
          <dataQualityIndicator name="Methodological appropriateness and consistency" value="Very good"/>
          <dataQualityIndicator name="Overall quality" value="Not evaluated / unknown"/>
        </dataQualityIndicators>
        <common:reviewDetails xml:lang="en">As part of the PlasticsEurope programme management and quality assurance, DEKRA Consulting GmbH conducted an external independent critical review of this work. The outcome of the critical review is reproduced below.


The subject of this critical review is the development of the Eco-profile for Styrene Acrylonitrile (SAN) and Acrylonitrile Butadiene Styrene (ABS).

The review process included various meetings/web-conferences between the LCA practitioner and the reviewer, which encompassed a model and database review and spot checks of data and calcula-tions. Furthermore, the final Eco-profile report was reviewed by the reviewer as well as industry partic-ipants involved in this project. All questions and recommendations were discussed with the LCA prac-titioner, and the report was adapted and revised accordingly.

Primary industry data were collected for the foreground processes comprising the production of SAN and ABS and taking into account the specific production processes of the four participating companies. Background data representing the main precursors as well as all other material and energy inputs were taken from the GaBi database. Primary industry data was collected from 5 sites producing SAN (one of which producing SAN from Alpha Methyl Styrene (AMS)) and five sites producing ABS, which lead to an estimated overall representativeness of &gt;90% of the installed European SAN and ABS production capacity. 

A critical aspect of the study is the use of the background dataset for butadiene which is an im-portant component (10-25%) of ABS production. It is a general principle of PlasticsEurope Eco-profiles that up-to-date Eco-profiles for precursor products should be used, if available. However, due to inter-operability issues between different LCA softwares and databases, a lack of information with regards to some inventory flows (e.g. water flows) and the use of different types of butadiene for ABS production, the integration of the Eco-profile for butadiene (PlasticsEurope 2012) caused difficulties. Consequently, GaBi datasets for the different types of butadiene were used accompanied by a detailed sensitivity analysis with the Eco-profile for butadiene for the main impact categories (please refer to the relevant section in the main report for more information). 

The potential environmental impacts for SAN and ABS are dominated by the precursor products styrene, acrylonitrile and butadiene (for ABS) across most impact categories. Electricity and thermal energy needed for SAN and ABS production also have a significant impact (about 7-8% for GWP). The results for ADP elements in case of ABS are also driven by the use of deionised water which requires salt. 

The Eco-profile report also includes a comparison of the results with the previous version of the SAN and ABS Eco-profiles. However, due to reasons outlined in the main report, a detailed analysis of the reasons for the differences is difficult and should be treated with great caution. 

The LCA practitioners have demonstrated very good competence and experience, with a track record of LCA projects in the chemical and plastics industry. The critical review confirms that this Eco-profile adheres to the rules set forth in the PlasticsEuropes Eco-profiles and Environmental Declarations  LCI Methodology and PCR for Uncompounded Polymer Resins and Reactive Polymer Precursors (PCR version 2.0, April 2011). As a result, this dataset is assessed to be a reliable and high quality representation of SAN and ABS produced in Europe.
</common:reviewDetails>
        <common:referenceToNameOfReviewerAndInstitution refObjectId="1ce916ab-6545-431c-a27d-47f0dbee9942" version="27.00.000" type="contact data set" uri="../contacts/1ce916ab-6545-431c-a27d-47f0dbee9942.xml">
          <common:shortDescription xml:lang="en">Matthias Schulz</common:shortDescription>
        </common:referenceToNameOfReviewerAndInstitution>
        <common:referenceToNameOfReviewerAndInstitution refObjectId="df43be2f-f81f-4248-8e29-9a3d27dc8167" version="27.00.000" type="contact data set" uri="../contacts/df43be2f-f81f-4248-8e29-9a3d27dc8167.xml">
          <common:shortDescription xml:lang="en">DEKRA Assurance Services GmbH</common:shortDescription>
        </common:referenceToNameOfReviewerAndInstitution>
      </review>
      <review type="Independent internal review">
        <common:scope name="Raw data">
          <common:method name="Validation of data sources"/>
          <common:method name="Sample tests on calculations"/>
          <common:method name="Cross-check with other source"/>
          <common:method name="Expert judgement"/>
        </common:scope>
        <common:scope name="Unit process(es), single operation">
          <common:method name="Energy balance"/>
          <common:method name="Element balance"/>
          <common:method name="Cross-check with other source"/>
          <common:method name="Cross-check with other data set"/>
          <common:method name="Expert judgement"/>
          <common:method name="Mass balance"/>
        </common:scope>
        <common:scope name="Unit process(es), black box">
          <common:method name="Energy balance"/>
          <common:method name="Element balance"/>
          <common:method name="Cross-check with other source"/>
          <common:method name="Cross-check with other data set"/>
          <common:method name="Expert judgement"/>
          <common:method name="Mass balance"/>
        </common:scope>
        <common:scope name="LCI results or Partly terminated system">
          <common:method name="Energy balance"/>
          <common:method name="Element balance"/>
          <common:method name="Cross-check with other source"/>
          <common:method name="Cross-check with other data set"/>
          <common:method name="Expert judgement"/>
          <common:method name="Mass balance"/>
        </common:scope>
        <common:scope name="LCIA results">
          <common:method name="Cross-check with other source"/>
          <common:method name="Cross-check with other data set"/>
          <common:method name="Expert judgement"/>
          <common:method name="Compliance with ISO 14040 to 14044"/>
        </common:scope>
        <common:scope name="Documentation">
          <common:method name="Expert judgement"/>
          <common:method name="Compliance with ISO 14040 to 14044"/>
          <common:method name="Documentation"/>
        </common:scope>
        <common:scope name="Life cycle inventory methods">
          <common:method name="Compliance with ISO 14040 to 14044"/>
        </common:scope>
        <common:scope name="LCIA results calculation">
          <common:method name="Expert judgement"/>
          <common:method name="Compliance with ISO 14040 to 14044"/>
        </common:scope>
        <common:scope name="Goal and scope definition">
          <common:method name="Expert judgement"/>
          <common:method name="Compliance with ISO 14040 to 14044"/>
        </common:scope>
        <dataQualityIndicators xmlns="http://lca.jrc.it/ILCD/Common">
          <dataQualityIndicator name="Technological representativeness" value="Good"/>
          <dataQualityIndicator name="Time representativeness" value="Very good"/>
          <dataQualityIndicator name="Geographical representativeness" value="Good"/>
          <dataQualityIndicator name="Completeness" value="Good"/>
          <dataQualityIndicator name="Precision" value="Good"/>
          <dataQualityIndicator name="Methodological appropriateness and consistency" value="Good"/>
          <dataQualityIndicator name="Overall quality" value="Good"/>
        </dataQualityIndicators>
        <common:reviewDetails xml:lang="en">All data sets in the GaBi Databases are constantly used, compared, benchmarked and reviewed by a broad GaBi user community. Calculated results are published frequently in various external, professional and third party LCA literature, papers, and other media within industry, academia and politics. The incorporation of feedback provided by the GaBi users is standard practice in the maintenance and update procedure, and leads to stable, quality-assured and constantly improved data.  The internal review is done with several iterative steps involving raw data validation, raw data documentation, representativeness, completeness and consistent modelling with regard to ISO 14040 and 14044. The data set documentation is correct in respect to the appropriateness of the information available. It includes all relevant information in relation to data quality and the scope of application of the respective LCI result.</common:reviewDetails>
        <common:referenceToNameOfReviewerAndInstitution refObjectId="623edf96-39d1-4e6f-9892-674c7228546b" version="27.00.000" type="contact data set" uri="../contacts/623edf96-39d1-4e6f-9892-674c7228546b.xml">
          <common:shortDescription xml:lang="en">PE INTERNATIONAL</common:shortDescription>
        </common:referenceToNameOfReviewerAndInstitution>
      </review>
    </validation>
    <complianceDeclarations>
      <compliance>
        <common:referenceToComplianceSystem refObjectId="6a08f8f9-58c3-492c-8c34-6df3dd69a326" version="27.00.000" type="source data set" uri="../sources/6a08f8f9-58c3-492c-8c34-6df3dd69a326.xml">
          <common:shortDescription xml:lang="en">GaBi conformity system</common:shortDescription>
        </common:referenceToComplianceSystem>
        <common:approvalOfOverallCompliance>Fully compliant</common:approvalOfOverallCompliance>
        <common:nomenclatureCompliance>Fully compliant</common:nomenclatureCompliance>
        <common:methodologicalCompliance>Fully compliant</common:methodologicalCompliance>
        <common:reviewCompliance>Fully compliant</common:reviewCompliance>
        <common:documentationCompliance>Fully compliant</common:documentationCompliance>
        <common:qualityCompliance>Not defined</common:qualityCompliance>
      </compliance>
      <compliance>
        <common:referenceToComplianceSystem refObjectId="10f467f6-6bee-4e67-a187-d06383b2984b" version="27.00.000" type="source data set" uri="../sources/10f467f6-6bee-4e67-a187-d06383b2984b.xml">
          <common:shortDescription xml:lang="en">UNEP SETAC Life Cycle Initiative</common:shortDescription>
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