Adaptation of ecoinvent database to Polish conditions: The case of wood production in the forest

Background, aims and scope This paper is based on the results of a project sponsored by the Ministry of Science and Higher Education and carried out by the Wood Technology Institute in Poznan, Poland. The main purpose of the project was to assess the environmental impact generated during the entire...

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Veröffentlicht in:The international journal of life cycle assessment 2008-06, Vol.13 (4), p.319-327
Hauptverfasser: Lewandowska, Anna, Wawrzynkiewicz, Zofia, Noskowiak, Andrzej, Foltynowicz, Zenon
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container_start_page 319
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creator Lewandowska, Anna
Wawrzynkiewicz, Zofia
Noskowiak, Andrzej
Foltynowicz, Zenon
description Background, aims and scope This paper is based on the results of a project sponsored by the Ministry of Science and Higher Education and carried out by the Wood Technology Institute in Poznan, Poland. The main purpose of the project was to assess the environmental impact generated during the entire life cycles of chosen wood products. Most of the data came from the Polish wood industry, but some of it was taken from the ecoinvent database, particularly data relating to forest processes. The data were not used as presented in the database but were properly adapted. The aim of the paper is to show how the ecoinvent’s initial assumptions have been changed and how the data were adapted. The influence of the adaptation on the characterization results is presented as well. Materials and methods The adaptation was performed in several steps: obtaining information about the principal assumptions of the ecoinvent database, gathering data appropriate to Polish conditions, changing the principal assumptions to include the Polish situation, calculating the new allocation and correction factors, forming the new inventory tables for round, industrial, and residual wood (softwood and hardwood), and calculating the characterization results to check the influence of the data adaptation on the life cycle assessment (LCA) final results. The following methods have been used: the economic allocation with the allocation correction to include mass, energy, and carbon dioxide uptake from nature and Ecoindicator99 method to assess the environmental impact. Results The study shows that differences exist between ecoinvent and Polish data for the wood production. Some of the differences are important and significantly impact the final results. The data differ in relation to many factors, for example: tree species, yield of forest, time from planting trees to final harvesting, length and width of forest roads or total area, and land use. The differences in the initial assumptions and further in the allocation factors result in changes of the inventory points and the characterization results. The relevant differences for round hardwood and residual hardwood are not observed. It is not, however, the case of the industrial hardwood where the visible difference exist. The results for all sorts of softwood are completely different and any similarities cannot be observed. Discussion At present, the total area of forest land in Poland is 9.0 million ha. This is equivalent to 28.8% of the cou
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The main purpose of the project was to assess the environmental impact generated during the entire life cycles of chosen wood products. Most of the data came from the Polish wood industry, but some of it was taken from the ecoinvent database, particularly data relating to forest processes. The data were not used as presented in the database but were properly adapted. The aim of the paper is to show how the ecoinvent’s initial assumptions have been changed and how the data were adapted. The influence of the adaptation on the characterization results is presented as well. Materials and methods The adaptation was performed in several steps: obtaining information about the principal assumptions of the ecoinvent database, gathering data appropriate to Polish conditions, changing the principal assumptions to include the Polish situation, calculating the new allocation and correction factors, forming the new inventory tables for round, industrial, and residual wood (softwood and hardwood), and calculating the characterization results to check the influence of the data adaptation on the life cycle assessment (LCA) final results. The following methods have been used: the economic allocation with the allocation correction to include mass, energy, and carbon dioxide uptake from nature and Ecoindicator99 method to assess the environmental impact. Results The study shows that differences exist between ecoinvent and Polish data for the wood production. Some of the differences are important and significantly impact the final results. The data differ in relation to many factors, for example: tree species, yield of forest, time from planting trees to final harvesting, length and width of forest roads or total area, and land use. The differences in the initial assumptions and further in the allocation factors result in changes of the inventory points and the characterization results. The relevant differences for round hardwood and residual hardwood are not observed. It is not, however, the case of the industrial hardwood where the visible difference exist. The results for all sorts of softwood are completely different and any similarities cannot be observed. Discussion At present, the total area of forest land in Poland is 9.0 million ha. This is equivalent to 28.8% of the country’s area. This means that the forest processes are important for the country. The study could be a part of a more general discussion about the suitability of data recognized by the database’s generators as representative for larger areas (Europe, Asia, the world). Conclusions The following conclusions could be formulated based on the results of the project: differences between countries always exist, and they can be a source of uncertainty, particularly if unspecific data are used. On the other hand, it is impossible to collect specific data for all inventory items included in the product system which is why LCA databases are needed. The following questions should be asked: how important is the discrepancy? What is its influence on the final results? Is it acceptable? There are some activities like electricity production where differences between countries can be crucial for the LCA final results. Recommendations and perspectives Two main recommendations could be formulated: the data taken from LCA databases should always be critically analyzed and reviewed to check if they are suitable for our case study, and, if possible, the adaptation to local or national conditions should be made. In Poland, the interest in LCA continues to grow; however, it is not easy for LCA practitioners to conduct LCAs because of companies’ skepticism and their reluctance to provide data. LCA databases are important sources of information. 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The main purpose of the project was to assess the environmental impact generated during the entire life cycles of chosen wood products. Most of the data came from the Polish wood industry, but some of it was taken from the ecoinvent database, particularly data relating to forest processes. The data were not used as presented in the database but were properly adapted. The aim of the paper is to show how the ecoinvent’s initial assumptions have been changed and how the data were adapted. The influence of the adaptation on the characterization results is presented as well. Materials and methods The adaptation was performed in several steps: obtaining information about the principal assumptions of the ecoinvent database, gathering data appropriate to Polish conditions, changing the principal assumptions to include the Polish situation, calculating the new allocation and correction factors, forming the new inventory tables for round, industrial, and residual wood (softwood and hardwood), and calculating the characterization results to check the influence of the data adaptation on the life cycle assessment (LCA) final results. The following methods have been used: the economic allocation with the allocation correction to include mass, energy, and carbon dioxide uptake from nature and Ecoindicator99 method to assess the environmental impact. Results The study shows that differences exist between ecoinvent and Polish data for the wood production. Some of the differences are important and significantly impact the final results. The data differ in relation to many factors, for example: tree species, yield of forest, time from planting trees to final harvesting, length and width of forest roads or total area, and land use. The differences in the initial assumptions and further in the allocation factors result in changes of the inventory points and the characterization results. The relevant differences for round hardwood and residual hardwood are not observed. It is not, however, the case of the industrial hardwood where the visible difference exist. The results for all sorts of softwood are completely different and any similarities cannot be observed. Discussion At present, the total area of forest land in Poland is 9.0 million ha. This is equivalent to 28.8% of the country’s area. This means that the forest processes are important for the country. The study could be a part of a more general discussion about the suitability of data recognized by the database’s generators as representative for larger areas (Europe, Asia, the world). Conclusions The following conclusions could be formulated based on the results of the project: differences between countries always exist, and they can be a source of uncertainty, particularly if unspecific data are used. On the other hand, it is impossible to collect specific data for all inventory items included in the product system which is why LCA databases are needed. The following questions should be asked: how important is the discrepancy? What is its influence on the final results? Is it acceptable? There are some activities like electricity production where differences between countries can be crucial for the LCA final results. Recommendations and perspectives Two main recommendations could be formulated: the data taken from LCA databases should always be critically analyzed and reviewed to check if they are suitable for our case study, and, if possible, the adaptation to local or national conditions should be made. In Poland, the interest in LCA continues to grow; however, it is not easy for LCA practitioners to conduct LCAs because of companies’ skepticism and their reluctance to provide data. LCA databases are important sources of information. 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The main purpose of the project was to assess the environmental impact generated during the entire life cycles of chosen wood products. Most of the data came from the Polish wood industry, but some of it was taken from the ecoinvent database, particularly data relating to forest processes. The data were not used as presented in the database but were properly adapted. The aim of the paper is to show how the ecoinvent’s initial assumptions have been changed and how the data were adapted. The influence of the adaptation on the characterization results is presented as well. Materials and methods The adaptation was performed in several steps: obtaining information about the principal assumptions of the ecoinvent database, gathering data appropriate to Polish conditions, changing the principal assumptions to include the Polish situation, calculating the new allocation and correction factors, forming the new inventory tables for round, industrial, and residual wood (softwood and hardwood), and calculating the characterization results to check the influence of the data adaptation on the life cycle assessment (LCA) final results. The following methods have been used: the economic allocation with the allocation correction to include mass, energy, and carbon dioxide uptake from nature and Ecoindicator99 method to assess the environmental impact. Results The study shows that differences exist between ecoinvent and Polish data for the wood production. Some of the differences are important and significantly impact the final results. The data differ in relation to many factors, for example: tree species, yield of forest, time from planting trees to final harvesting, length and width of forest roads or total area, and land use. The differences in the initial assumptions and further in the allocation factors result in changes of the inventory points and the characterization results. The relevant differences for round hardwood and residual hardwood are not observed. It is not, however, the case of the industrial hardwood where the visible difference exist. The results for all sorts of softwood are completely different and any similarities cannot be observed. Discussion At present, the total area of forest land in Poland is 9.0 million ha. This is equivalent to 28.8% of the country’s area. This means that the forest processes are important for the country. The study could be a part of a more general discussion about the suitability of data recognized by the database’s generators as representative for larger areas (Europe, Asia, the world). Conclusions The following conclusions could be formulated based on the results of the project: differences between countries always exist, and they can be a source of uncertainty, particularly if unspecific data are used. On the other hand, it is impossible to collect specific data for all inventory items included in the product system which is why LCA databases are needed. The following questions should be asked: how important is the discrepancy? What is its influence on the final results? Is it acceptable? There are some activities like electricity production where differences between countries can be crucial for the LCA final results. Recommendations and perspectives Two main recommendations could be formulated: the data taken from LCA databases should always be critically analyzed and reviewed to check if they are suitable for our case study, and, if possible, the adaptation to local or national conditions should be made. In Poland, the interest in LCA continues to grow; however, it is not easy for LCA practitioners to conduct LCAs because of companies’ skepticism and their reluctance to provide data. LCA databases are important sources of information. A review of the most popular LCA databases could be a good line of further improvement to make LCA studies more relevant and reliable.</abstract><cop>Berlin/Heidelberg</cop><pub>Springer-Verlag</pub><doi>10.1007/s11367-008-0010-3</doi><tpages>9</tpages></addata></record>
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subjects Adaptation
Carbon dioxide
Earth and Environmental Science
Education
Electric power generation
Environment
Environmental assessment
Environmental Chemistry
Environmental Economics
Environmental Engineering/Biotechnology
Environmental impact
Forests
Hardwoods
Land use
Life cycle analysis
Life cycles
Plant species
Softwoods
Studies
Tree planting
Wood
Wood and Other Renewable Resources • Case Study
Wood products
title Adaptation of ecoinvent database to Polish conditions: The case of wood production in the forest
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