Waste treatment in product specific life cycle inventories
Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL)...
Ausführliche Beschreibung
Autor*in: |
Kremer, Markus [verfasserIn] |
---|
Format: |
Artikel |
---|---|
Sprache: |
Englisch |
Erschienen: |
1998 |
---|
Schlagwörter: |
LCA, waste disposal, incineration material-related modelling, waste incineration municipal solid waste incineration, LCA |
---|
Anmerkung: |
© Ecomed Publishers 1998 |
---|
Übergeordnetes Werk: |
Enthalten in: The international journal of life cycle assessment - Ecomed, 1996, 3(1998), 1 vom: Jan., Seite 47-55 |
---|---|
Übergeordnetes Werk: |
volume:3 ; year:1998 ; number:1 ; month:01 ; pages:47-55 |
Links: |
---|
DOI / URN: |
10.1007/BF02978452 |
---|
Katalog-ID: |
OLC2051187576 |
---|
LEADER | 01000caa a22002652 4500 | ||
---|---|---|---|
001 | OLC2051187576 | ||
003 | DE-627 | ||
005 | 20230504090306.0 | ||
007 | tu | ||
008 | 200820s1998 xx ||||| 00| ||eng c | ||
024 | 7 | |a 10.1007/BF02978452 |2 doi | |
035 | |a (DE-627)OLC2051187576 | ||
035 | |a (DE-He213)BF02978452-p | ||
040 | |a DE-627 |b ger |c DE-627 |e rakwb | ||
041 | |a eng | ||
082 | 0 | 4 | |a 650 |a 330 |a 333.7 |q VZ |
082 | 0 | 4 | |a 690 |q VZ |
100 | 1 | |a Kremer, Markus |e verfasserin |4 aut | |
245 | 1 | 0 | |a Waste treatment in product specific life cycle inventories |
264 | 1 | |c 1998 | |
336 | |a Text |b txt |2 rdacontent | ||
337 | |a ohne Hilfsmittel zu benutzen |b n |2 rdamedia | ||
338 | |a Band |b nc |2 rdacarrier | ||
500 | |a © Ecomed Publishers 1998 | ||
520 | |a Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process. | ||
650 | 4 | |a LCA, waste disposal, incineration | |
650 | 4 | |a landfill, waste, LCA | |
650 | 4 | |a material-related modelling, waste incineration | |
650 | 4 | |a municipal solid waste incineration, LCA | |
650 | 4 | |a waste disposal, material-related modelling, LCA | |
650 | 4 | |a waste incineration, material-related modelling, LCA | |
700 | 1 | |a Goldhan, Gertraud |4 aut | |
700 | 1 | |a Heyde, Michael |4 aut | |
773 | 0 | 8 | |i Enthalten in |t The international journal of life cycle assessment |d Ecomed, 1996 |g 3(1998), 1 vom: Jan., Seite 47-55 |w (DE-627)211584533 |w (DE-600)1319419-7 |w (DE-576)059728728 |x 0948-3349 |7 nnns |
773 | 1 | 8 | |g volume:3 |g year:1998 |g number:1 |g month:01 |g pages:47-55 |
856 | 4 | 1 | |u https://doi.org/10.1007/BF02978452 |z lizenzpflichtig |3 Volltext |
912 | |a GBV_USEFLAG_A | ||
912 | |a SYSFLAG_A | ||
912 | |a GBV_OLC | ||
912 | |a SSG-OLC-UMW | ||
912 | |a SSG-OLC-ARC | ||
912 | |a SSG-OLC-TEC | ||
912 | |a SSG-OPC-FOR | ||
912 | |a GBV_ILN_30 | ||
912 | |a GBV_ILN_70 | ||
912 | |a GBV_ILN_252 | ||
912 | |a GBV_ILN_267 | ||
912 | |a GBV_ILN_2016 | ||
912 | |a GBV_ILN_4012 | ||
912 | |a GBV_ILN_4046 | ||
912 | |a GBV_ILN_4305 | ||
912 | |a GBV_ILN_4313 | ||
951 | |a AR | ||
952 | |d 3 |j 1998 |e 1 |c 01 |h 47-55 |
author_variant |
m k mk g g gg m h mh |
---|---|
matchkey_str |
article:09483349:1998----::attetetnrdcseiilfc |
hierarchy_sort_str |
1998 |
publishDate |
1998 |
allfields |
10.1007/BF02978452 doi (DE-627)OLC2051187576 (DE-He213)BF02978452-p DE-627 ger DE-627 rakwb eng 650 330 333.7 VZ 690 VZ Kremer, Markus verfasserin aut Waste treatment in product specific life cycle inventories 1998 Text txt rdacontent ohne Hilfsmittel zu benutzen n rdamedia Band nc rdacarrier © Ecomed Publishers 1998 Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process. LCA, waste disposal, incineration landfill, waste, LCA material-related modelling, waste incineration municipal solid waste incineration, LCA waste disposal, material-related modelling, LCA waste incineration, material-related modelling, LCA Goldhan, Gertraud aut Heyde, Michael aut Enthalten in The international journal of life cycle assessment Ecomed, 1996 3(1998), 1 vom: Jan., Seite 47-55 (DE-627)211584533 (DE-600)1319419-7 (DE-576)059728728 0948-3349 nnns volume:3 year:1998 number:1 month:01 pages:47-55 https://doi.org/10.1007/BF02978452 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_OLC SSG-OLC-UMW SSG-OLC-ARC SSG-OLC-TEC SSG-OPC-FOR GBV_ILN_30 GBV_ILN_70 GBV_ILN_252 GBV_ILN_267 GBV_ILN_2016 GBV_ILN_4012 GBV_ILN_4046 GBV_ILN_4305 GBV_ILN_4313 AR 3 1998 1 01 47-55 |
spelling |
10.1007/BF02978452 doi (DE-627)OLC2051187576 (DE-He213)BF02978452-p DE-627 ger DE-627 rakwb eng 650 330 333.7 VZ 690 VZ Kremer, Markus verfasserin aut Waste treatment in product specific life cycle inventories 1998 Text txt rdacontent ohne Hilfsmittel zu benutzen n rdamedia Band nc rdacarrier © Ecomed Publishers 1998 Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process. LCA, waste disposal, incineration landfill, waste, LCA material-related modelling, waste incineration municipal solid waste incineration, LCA waste disposal, material-related modelling, LCA waste incineration, material-related modelling, LCA Goldhan, Gertraud aut Heyde, Michael aut Enthalten in The international journal of life cycle assessment Ecomed, 1996 3(1998), 1 vom: Jan., Seite 47-55 (DE-627)211584533 (DE-600)1319419-7 (DE-576)059728728 0948-3349 nnns volume:3 year:1998 number:1 month:01 pages:47-55 https://doi.org/10.1007/BF02978452 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_OLC SSG-OLC-UMW SSG-OLC-ARC SSG-OLC-TEC SSG-OPC-FOR GBV_ILN_30 GBV_ILN_70 GBV_ILN_252 GBV_ILN_267 GBV_ILN_2016 GBV_ILN_4012 GBV_ILN_4046 GBV_ILN_4305 GBV_ILN_4313 AR 3 1998 1 01 47-55 |
allfields_unstemmed |
10.1007/BF02978452 doi (DE-627)OLC2051187576 (DE-He213)BF02978452-p DE-627 ger DE-627 rakwb eng 650 330 333.7 VZ 690 VZ Kremer, Markus verfasserin aut Waste treatment in product specific life cycle inventories 1998 Text txt rdacontent ohne Hilfsmittel zu benutzen n rdamedia Band nc rdacarrier © Ecomed Publishers 1998 Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process. LCA, waste disposal, incineration landfill, waste, LCA material-related modelling, waste incineration municipal solid waste incineration, LCA waste disposal, material-related modelling, LCA waste incineration, material-related modelling, LCA Goldhan, Gertraud aut Heyde, Michael aut Enthalten in The international journal of life cycle assessment Ecomed, 1996 3(1998), 1 vom: Jan., Seite 47-55 (DE-627)211584533 (DE-600)1319419-7 (DE-576)059728728 0948-3349 nnns volume:3 year:1998 number:1 month:01 pages:47-55 https://doi.org/10.1007/BF02978452 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_OLC SSG-OLC-UMW SSG-OLC-ARC SSG-OLC-TEC SSG-OPC-FOR GBV_ILN_30 GBV_ILN_70 GBV_ILN_252 GBV_ILN_267 GBV_ILN_2016 GBV_ILN_4012 GBV_ILN_4046 GBV_ILN_4305 GBV_ILN_4313 AR 3 1998 1 01 47-55 |
allfieldsGer |
10.1007/BF02978452 doi (DE-627)OLC2051187576 (DE-He213)BF02978452-p DE-627 ger DE-627 rakwb eng 650 330 333.7 VZ 690 VZ Kremer, Markus verfasserin aut Waste treatment in product specific life cycle inventories 1998 Text txt rdacontent ohne Hilfsmittel zu benutzen n rdamedia Band nc rdacarrier © Ecomed Publishers 1998 Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process. LCA, waste disposal, incineration landfill, waste, LCA material-related modelling, waste incineration municipal solid waste incineration, LCA waste disposal, material-related modelling, LCA waste incineration, material-related modelling, LCA Goldhan, Gertraud aut Heyde, Michael aut Enthalten in The international journal of life cycle assessment Ecomed, 1996 3(1998), 1 vom: Jan., Seite 47-55 (DE-627)211584533 (DE-600)1319419-7 (DE-576)059728728 0948-3349 nnns volume:3 year:1998 number:1 month:01 pages:47-55 https://doi.org/10.1007/BF02978452 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_OLC SSG-OLC-UMW SSG-OLC-ARC SSG-OLC-TEC SSG-OPC-FOR GBV_ILN_30 GBV_ILN_70 GBV_ILN_252 GBV_ILN_267 GBV_ILN_2016 GBV_ILN_4012 GBV_ILN_4046 GBV_ILN_4305 GBV_ILN_4313 AR 3 1998 1 01 47-55 |
allfieldsSound |
10.1007/BF02978452 doi (DE-627)OLC2051187576 (DE-He213)BF02978452-p DE-627 ger DE-627 rakwb eng 650 330 333.7 VZ 690 VZ Kremer, Markus verfasserin aut Waste treatment in product specific life cycle inventories 1998 Text txt rdacontent ohne Hilfsmittel zu benutzen n rdamedia Band nc rdacarrier © Ecomed Publishers 1998 Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process. LCA, waste disposal, incineration landfill, waste, LCA material-related modelling, waste incineration municipal solid waste incineration, LCA waste disposal, material-related modelling, LCA waste incineration, material-related modelling, LCA Goldhan, Gertraud aut Heyde, Michael aut Enthalten in The international journal of life cycle assessment Ecomed, 1996 3(1998), 1 vom: Jan., Seite 47-55 (DE-627)211584533 (DE-600)1319419-7 (DE-576)059728728 0948-3349 nnns volume:3 year:1998 number:1 month:01 pages:47-55 https://doi.org/10.1007/BF02978452 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_OLC SSG-OLC-UMW SSG-OLC-ARC SSG-OLC-TEC SSG-OPC-FOR GBV_ILN_30 GBV_ILN_70 GBV_ILN_252 GBV_ILN_267 GBV_ILN_2016 GBV_ILN_4012 GBV_ILN_4046 GBV_ILN_4305 GBV_ILN_4313 AR 3 1998 1 01 47-55 |
language |
English |
source |
Enthalten in The international journal of life cycle assessment 3(1998), 1 vom: Jan., Seite 47-55 volume:3 year:1998 number:1 month:01 pages:47-55 |
sourceStr |
Enthalten in The international journal of life cycle assessment 3(1998), 1 vom: Jan., Seite 47-55 volume:3 year:1998 number:1 month:01 pages:47-55 |
format_phy_str_mv |
Article |
institution |
findex.gbv.de |
topic_facet |
LCA, waste disposal, incineration landfill, waste, LCA material-related modelling, waste incineration municipal solid waste incineration, LCA waste disposal, material-related modelling, LCA waste incineration, material-related modelling, LCA |
dewey-raw |
650 |
isfreeaccess_bool |
false |
container_title |
The international journal of life cycle assessment |
authorswithroles_txt_mv |
Kremer, Markus @@aut@@ Goldhan, Gertraud @@aut@@ Heyde, Michael @@aut@@ |
publishDateDaySort_date |
1998-01-01T00:00:00Z |
hierarchy_top_id |
211584533 |
dewey-sort |
3650 |
id |
OLC2051187576 |
language_de |
englisch |
fullrecord |
<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">OLC2051187576</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230504090306.0</controlfield><controlfield tag="007">tu</controlfield><controlfield tag="008">200820s1998 xx ||||| 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/BF02978452</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)OLC2051187576</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-He213)BF02978452-p</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="082" ind1="0" ind2="4"><subfield code="a">650</subfield><subfield code="a">330</subfield><subfield code="a">333.7</subfield><subfield code="q">VZ</subfield></datafield><datafield tag="082" ind1="0" ind2="4"><subfield code="a">690</subfield><subfield code="q">VZ</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Kremer, Markus</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Waste treatment in product specific life cycle inventories</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">1998</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">ohne Hilfsmittel zu benutzen</subfield><subfield code="b">n</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Band</subfield><subfield code="b">nc</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="500" ind1=" " ind2=" "><subfield code="a">© Ecomed Publishers 1998</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">LCA, waste disposal, incineration</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">landfill, waste, LCA</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">material-related modelling, waste incineration</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">municipal solid waste incineration, LCA</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">waste disposal, material-related modelling, LCA</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">waste incineration, material-related modelling, LCA</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Goldhan, Gertraud</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Heyde, Michael</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">Enthalten in</subfield><subfield code="t">The international journal of life cycle assessment</subfield><subfield code="d">Ecomed, 1996</subfield><subfield code="g">3(1998), 1 vom: Jan., Seite 47-55</subfield><subfield code="w">(DE-627)211584533</subfield><subfield code="w">(DE-600)1319419-7</subfield><subfield code="w">(DE-576)059728728</subfield><subfield code="x">0948-3349</subfield><subfield code="7">nnns</subfield></datafield><datafield tag="773" ind1="1" ind2="8"><subfield code="g">volume:3</subfield><subfield code="g">year:1998</subfield><subfield code="g">number:1</subfield><subfield code="g">month:01</subfield><subfield code="g">pages:47-55</subfield></datafield><datafield tag="856" ind1="4" ind2="1"><subfield code="u">https://doi.org/10.1007/BF02978452</subfield><subfield code="z">lizenzpflichtig</subfield><subfield code="3">Volltext</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_USEFLAG_A</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SYSFLAG_A</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_OLC</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-UMW</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-ARC</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-TEC</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OPC-FOR</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_30</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_70</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_252</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_267</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2016</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4012</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4046</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4305</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4313</subfield></datafield><datafield tag="951" ind1=" " ind2=" "><subfield code="a">AR</subfield></datafield><datafield tag="952" ind1=" " ind2=" "><subfield code="d">3</subfield><subfield code="j">1998</subfield><subfield code="e">1</subfield><subfield code="c">01</subfield><subfield code="h">47-55</subfield></datafield></record></collection>
|
author |
Kremer, Markus |
spellingShingle |
Kremer, Markus ddc 650 ddc 690 misc LCA, waste disposal, incineration misc landfill, waste, LCA misc material-related modelling, waste incineration misc municipal solid waste incineration, LCA misc waste disposal, material-related modelling, LCA misc waste incineration, material-related modelling, LCA Waste treatment in product specific life cycle inventories |
authorStr |
Kremer, Markus |
ppnlink_with_tag_str_mv |
@@773@@(DE-627)211584533 |
format |
Article |
dewey-ones |
650 - Management & auxiliary services 330 - Economics 333 - Economics of land & energy 690 - Buildings |
delete_txt_mv |
keep |
author_role |
aut aut aut |
collection |
OLC |
remote_str |
false |
illustrated |
Not Illustrated |
issn |
0948-3349 |
topic_title |
650 330 333.7 VZ 690 VZ Waste treatment in product specific life cycle inventories LCA, waste disposal, incineration landfill, waste, LCA material-related modelling, waste incineration municipal solid waste incineration, LCA waste disposal, material-related modelling, LCA waste incineration, material-related modelling, LCA |
topic |
ddc 650 ddc 690 misc LCA, waste disposal, incineration misc landfill, waste, LCA misc material-related modelling, waste incineration misc municipal solid waste incineration, LCA misc waste disposal, material-related modelling, LCA misc waste incineration, material-related modelling, LCA |
topic_unstemmed |
ddc 650 ddc 690 misc LCA, waste disposal, incineration misc landfill, waste, LCA misc material-related modelling, waste incineration misc municipal solid waste incineration, LCA misc waste disposal, material-related modelling, LCA misc waste incineration, material-related modelling, LCA |
topic_browse |
ddc 650 ddc 690 misc LCA, waste disposal, incineration misc landfill, waste, LCA misc material-related modelling, waste incineration misc municipal solid waste incineration, LCA misc waste disposal, material-related modelling, LCA misc waste incineration, material-related modelling, LCA |
format_facet |
Aufsätze Gedruckte Aufsätze |
format_main_str_mv |
Text Zeitschrift/Artikel |
carriertype_str_mv |
nc |
hierarchy_parent_title |
The international journal of life cycle assessment |
hierarchy_parent_id |
211584533 |
dewey-tens |
650 - Management & public relations 330 - Economics 690 - Building & construction |
hierarchy_top_title |
The international journal of life cycle assessment |
isfreeaccess_txt |
false |
familylinks_str_mv |
(DE-627)211584533 (DE-600)1319419-7 (DE-576)059728728 |
title |
Waste treatment in product specific life cycle inventories |
ctrlnum |
(DE-627)OLC2051187576 (DE-He213)BF02978452-p |
title_full |
Waste treatment in product specific life cycle inventories |
author_sort |
Kremer, Markus |
journal |
The international journal of life cycle assessment |
journalStr |
The international journal of life cycle assessment |
lang_code |
eng |
isOA_bool |
false |
dewey-hundreds |
600 - Technology 300 - Social sciences |
recordtype |
marc |
publishDateSort |
1998 |
contenttype_str_mv |
txt |
container_start_page |
47 |
author_browse |
Kremer, Markus Goldhan, Gertraud Heyde, Michael |
container_volume |
3 |
class |
650 330 333.7 VZ 690 VZ |
format_se |
Aufsätze |
author-letter |
Kremer, Markus |
doi_str_mv |
10.1007/BF02978452 |
dewey-full |
650 330 333.7 690 |
title_sort |
waste treatment in product specific life cycle inventories |
title_auth |
Waste treatment in product specific life cycle inventories |
abstract |
Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process. © Ecomed Publishers 1998 |
abstractGer |
Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process. © Ecomed Publishers 1998 |
abstract_unstemmed |
Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process. © Ecomed Publishers 1998 |
collection_details |
GBV_USEFLAG_A SYSFLAG_A GBV_OLC SSG-OLC-UMW SSG-OLC-ARC SSG-OLC-TEC SSG-OPC-FOR GBV_ILN_30 GBV_ILN_70 GBV_ILN_252 GBV_ILN_267 GBV_ILN_2016 GBV_ILN_4012 GBV_ILN_4046 GBV_ILN_4305 GBV_ILN_4313 |
container_issue |
1 |
title_short |
Waste treatment in product specific life cycle inventories |
url |
https://doi.org/10.1007/BF02978452 |
remote_bool |
false |
author2 |
Goldhan, Gertraud Heyde, Michael |
author2Str |
Goldhan, Gertraud Heyde, Michael |
ppnlink |
211584533 |
mediatype_str_mv |
n |
isOA_txt |
false |
hochschulschrift_bool |
false |
doi_str |
10.1007/BF02978452 |
up_date |
2024-07-04T03:46:42.184Z |
_version_ |
1803618670031667200 |
fullrecord_marcxml |
<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">OLC2051187576</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230504090306.0</controlfield><controlfield tag="007">tu</controlfield><controlfield tag="008">200820s1998 xx ||||| 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/BF02978452</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)OLC2051187576</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-He213)BF02978452-p</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="082" ind1="0" ind2="4"><subfield code="a">650</subfield><subfield code="a">330</subfield><subfield code="a">333.7</subfield><subfield code="q">VZ</subfield></datafield><datafield tag="082" ind1="0" ind2="4"><subfield code="a">690</subfield><subfield code="q">VZ</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Kremer, Markus</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Waste treatment in product specific life cycle inventories</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">1998</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">ohne Hilfsmittel zu benutzen</subfield><subfield code="b">n</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Band</subfield><subfield code="b">nc</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="500" ind1=" " ind2=" "><subfield code="a">© Ecomed Publishers 1998</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract In product specific Life Cycle Assessment the environmental impacts resulting from the disposal of the product under study frequently have a strong influence on the overall result. Since the major disposal system - the Municipal Solid Waste Incineration (MSWI) and the Sanitary Landfill (SL) - are complex processes specially adapted for the treatment of a large variety of different types of waste with varying input composition, the direct determination of the environmental impacts coming from a single input component for example by measurements is not practicable. Two methods (Part I: MSWI, Part II: SL) of allocating the inventory positions caused by the processes MSWI and SL to individual input fractions are presented. The approaches described are based on process modelling for the calculation of the material and energy inputs and outputs of the disposal systems. For the MSWI process the material related allocation is carried out by means of a study of difference: The input/output balance is calculated with the process model for two variants with different input compositions. The input for the first variant consists of waste of average composition enlarged by a small amount of special waste fraction under study. In the second variant the calculation is done with an input consisting only of waste with average composition. The difference formed between the results of process calculation for both variants gives the effects of the treatment of the waste fraction under study in the disposal process.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">LCA, waste disposal, incineration</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">landfill, waste, LCA</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">material-related modelling, waste incineration</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">municipal solid waste incineration, LCA</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">waste disposal, material-related modelling, LCA</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">waste incineration, material-related modelling, LCA</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Goldhan, Gertraud</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Heyde, Michael</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">Enthalten in</subfield><subfield code="t">The international journal of life cycle assessment</subfield><subfield code="d">Ecomed, 1996</subfield><subfield code="g">3(1998), 1 vom: Jan., Seite 47-55</subfield><subfield code="w">(DE-627)211584533</subfield><subfield code="w">(DE-600)1319419-7</subfield><subfield code="w">(DE-576)059728728</subfield><subfield code="x">0948-3349</subfield><subfield code="7">nnns</subfield></datafield><datafield tag="773" ind1="1" ind2="8"><subfield code="g">volume:3</subfield><subfield code="g">year:1998</subfield><subfield code="g">number:1</subfield><subfield code="g">month:01</subfield><subfield code="g">pages:47-55</subfield></datafield><datafield tag="856" ind1="4" ind2="1"><subfield code="u">https://doi.org/10.1007/BF02978452</subfield><subfield code="z">lizenzpflichtig</subfield><subfield code="3">Volltext</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_USEFLAG_A</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SYSFLAG_A</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_OLC</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-UMW</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-ARC</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OLC-TEC</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">SSG-OPC-FOR</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_30</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_70</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_252</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_267</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_2016</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4012</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4046</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4305</subfield></datafield><datafield tag="912" ind1=" " ind2=" "><subfield code="a">GBV_ILN_4313</subfield></datafield><datafield tag="951" ind1=" " ind2=" "><subfield code="a">AR</subfield></datafield><datafield tag="952" ind1=" " ind2=" "><subfield code="d">3</subfield><subfield code="j">1998</subfield><subfield code="e">1</subfield><subfield code="c">01</subfield><subfield code="h">47-55</subfield></datafield></record></collection>
|
score |
7.4030848 |