Life cycle assessment at nanoscale: review and recommendations
Purpose The need for a systematic evaluation of the human and environmental impacts of engineered nanomaterials (ENMs) has been widely recognized, and a growing body of literature is available endorsing life cycle assessment (LCA) as a valid tool for the same. The purpose of this study is to evaluat...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Gavankar, Sheetal [verfasserIn] Suh, Sangwon [verfasserIn] Keller, Arturo F. [verfasserIn] |
|---|
| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2012 |
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| Schlagwörter: |
LCA of engineered nanomaterials LCI of engineered nanomaterials |
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| Übergeordnetes Werk: |
Enthalten in: The international journal of life cycle assessment - Berlin : Springer, 1996, 17(2012), 3 vom: 11. Jan., Seite 295-303 |
|---|---|
| Übergeordnetes Werk: |
volume:17 ; year:2012 ; number:3 ; day:11 ; month:01 ; pages:295-303 |
| Links: |
|---|
| DOI / URN: |
10.1007/s11367-011-0368-5 |
|---|
| Katalog-ID: |
SPR018929230 |
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| 520 | |a Purpose The need for a systematic evaluation of the human and environmental impacts of engineered nanomaterials (ENMs) has been widely recognized, and a growing body of literature is available endorsing life cycle assessment (LCA) as a valid tool for the same. The purpose of this study is to evaluate how the nano-specific environmental assessments are being done within the existing framework of life cycle inventory and impact assessment and whether these frameworks are valid and/or whether they can be modified for nano-evaluations. Method In order to do that, we reviewed the state-of-the-art literature on environmental impacts of nanomaterials and life cycle assessment studies on ENMs and nanoproducts. We evaluated the major characteristics and mechanisms under which nanomaterials affect the environment and whether these characteristics and mechanisms can be adequately addressed with current life cycle inventories and impact assessment practices. We also discuss whether the current data and knowledge accumulated around fate, transport, and toxicity of nanomaterials can be used to perform an interim evaluation while more data are being generated. Observations and recommendations We found that while there is plenty of literature available promoting LCA as a viable tool for ENMs and nanoproducts, there are only a handful of studies where at least some parts of life cycle were evaluated for nanoproducts or nanomaterial. None of the LCA studies on ENMs or nanoproducts that we came across assessed nano-specific fate, transport, and toxicity effects as part of their evaluation citing the lack of data as the primary reason. However, our literature review indicates that nano-LCA studies need not omit the assessment of nanomaterials’ human health and environmental impact due to incomplete data. There is some evidence that scalability may exist in certain types of nanomaterial, and traditional characterization can be applied even below 100 nm up to the scalability breakdown limits. For the size range where the scalability cannot be established, it may be more appropriate to explore empirical relationships, though possibly crude, between nanomaterial properties and their impact on human health and environment. Empirical relationships thus derived can serve as valid input for assessment until specific data points for nanomaterial fate, transport, and toxicity become available. Finally, where there is no quantitative data available, qualitative inferences may be drawn based on the known information of the nanomaterial and its potential release pathways. | ||
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10.1007/s11367-011-0368-5 doi (DE-627)SPR018929230 (SPR)s11367-011-0368-5-e DE-627 ger DE-627 rakwb eng 690 ASE 43.33 bkl 85.15 bkl 85.35 bkl Gavankar, Sheetal verfasserin aut Life cycle assessment at nanoscale: review and recommendations 2012 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The need for a systematic evaluation of the human and environmental impacts of engineered nanomaterials (ENMs) has been widely recognized, and a growing body of literature is available endorsing life cycle assessment (LCA) as a valid tool for the same. The purpose of this study is to evaluate how the nano-specific environmental assessments are being done within the existing framework of life cycle inventory and impact assessment and whether these frameworks are valid and/or whether they can be modified for nano-evaluations. Method In order to do that, we reviewed the state-of-the-art literature on environmental impacts of nanomaterials and life cycle assessment studies on ENMs and nanoproducts. We evaluated the major characteristics and mechanisms under which nanomaterials affect the environment and whether these characteristics and mechanisms can be adequately addressed with current life cycle inventories and impact assessment practices. We also discuss whether the current data and knowledge accumulated around fate, transport, and toxicity of nanomaterials can be used to perform an interim evaluation while more data are being generated. Observations and recommendations We found that while there is plenty of literature available promoting LCA as a viable tool for ENMs and nanoproducts, there are only a handful of studies where at least some parts of life cycle were evaluated for nanoproducts or nanomaterial. None of the LCA studies on ENMs or nanoproducts that we came across assessed nano-specific fate, transport, and toxicity effects as part of their evaluation citing the lack of data as the primary reason. However, our literature review indicates that nano-LCA studies need not omit the assessment of nanomaterials’ human health and environmental impact due to incomplete data. There is some evidence that scalability may exist in certain types of nanomaterial, and traditional characterization can be applied even below 100 nm up to the scalability breakdown limits. For the size range where the scalability cannot be established, it may be more appropriate to explore empirical relationships, though possibly crude, between nanomaterial properties and their impact on human health and environment. Empirical relationships thus derived can serve as valid input for assessment until specific data points for nanomaterial fate, transport, and toxicity become available. Finally, where there is no quantitative data available, qualitative inferences may be drawn based on the known information of the nanomaterial and its potential release pathways. LCA of engineered nanomaterials (dpeaa)DE-He213 LCI of engineered nanomaterials (dpeaa)DE-He213 LCIA of engineered nanomaterials (dpeaa)DE-He213 Nanomaterial fate (dpeaa)DE-He213 Transport (dpeaa)DE-He213 Toxicity (dpeaa)DE-He213 Suh, Sangwon verfasserin aut Keller, Arturo F. verfasserin aut Enthalten in The international journal of life cycle assessment Berlin : Springer, 1996 17(2012), 3 vom: 11. Jan., Seite 295-303 (DE-627)313652961 (DE-600)2009386-X 1614-7502 nnns volume:17 year:2012 number:3 day:11 month:01 pages:295-303 https://dx.doi.org/10.1007/s11367-011-0368-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.33 ASE 85.15 ASE 85.35 ASE AR 17 2012 3 11 01 295-303 |
| spelling |
10.1007/s11367-011-0368-5 doi (DE-627)SPR018929230 (SPR)s11367-011-0368-5-e DE-627 ger DE-627 rakwb eng 690 ASE 43.33 bkl 85.15 bkl 85.35 bkl Gavankar, Sheetal verfasserin aut Life cycle assessment at nanoscale: review and recommendations 2012 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The need for a systematic evaluation of the human and environmental impacts of engineered nanomaterials (ENMs) has been widely recognized, and a growing body of literature is available endorsing life cycle assessment (LCA) as a valid tool for the same. The purpose of this study is to evaluate how the nano-specific environmental assessments are being done within the existing framework of life cycle inventory and impact assessment and whether these frameworks are valid and/or whether they can be modified for nano-evaluations. Method In order to do that, we reviewed the state-of-the-art literature on environmental impacts of nanomaterials and life cycle assessment studies on ENMs and nanoproducts. We evaluated the major characteristics and mechanisms under which nanomaterials affect the environment and whether these characteristics and mechanisms can be adequately addressed with current life cycle inventories and impact assessment practices. We also discuss whether the current data and knowledge accumulated around fate, transport, and toxicity of nanomaterials can be used to perform an interim evaluation while more data are being generated. Observations and recommendations We found that while there is plenty of literature available promoting LCA as a viable tool for ENMs and nanoproducts, there are only a handful of studies where at least some parts of life cycle were evaluated for nanoproducts or nanomaterial. None of the LCA studies on ENMs or nanoproducts that we came across assessed nano-specific fate, transport, and toxicity effects as part of their evaluation citing the lack of data as the primary reason. However, our literature review indicates that nano-LCA studies need not omit the assessment of nanomaterials’ human health and environmental impact due to incomplete data. There is some evidence that scalability may exist in certain types of nanomaterial, and traditional characterization can be applied even below 100 nm up to the scalability breakdown limits. For the size range where the scalability cannot be established, it may be more appropriate to explore empirical relationships, though possibly crude, between nanomaterial properties and their impact on human health and environment. Empirical relationships thus derived can serve as valid input for assessment until specific data points for nanomaterial fate, transport, and toxicity become available. Finally, where there is no quantitative data available, qualitative inferences may be drawn based on the known information of the nanomaterial and its potential release pathways. LCA of engineered nanomaterials (dpeaa)DE-He213 LCI of engineered nanomaterials (dpeaa)DE-He213 LCIA of engineered nanomaterials (dpeaa)DE-He213 Nanomaterial fate (dpeaa)DE-He213 Transport (dpeaa)DE-He213 Toxicity (dpeaa)DE-He213 Suh, Sangwon verfasserin aut Keller, Arturo F. verfasserin aut Enthalten in The international journal of life cycle assessment Berlin : Springer, 1996 17(2012), 3 vom: 11. Jan., Seite 295-303 (DE-627)313652961 (DE-600)2009386-X 1614-7502 nnns volume:17 year:2012 number:3 day:11 month:01 pages:295-303 https://dx.doi.org/10.1007/s11367-011-0368-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.33 ASE 85.15 ASE 85.35 ASE AR 17 2012 3 11 01 295-303 |
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10.1007/s11367-011-0368-5 doi (DE-627)SPR018929230 (SPR)s11367-011-0368-5-e DE-627 ger DE-627 rakwb eng 690 ASE 43.33 bkl 85.15 bkl 85.35 bkl Gavankar, Sheetal verfasserin aut Life cycle assessment at nanoscale: review and recommendations 2012 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The need for a systematic evaluation of the human and environmental impacts of engineered nanomaterials (ENMs) has been widely recognized, and a growing body of literature is available endorsing life cycle assessment (LCA) as a valid tool for the same. The purpose of this study is to evaluate how the nano-specific environmental assessments are being done within the existing framework of life cycle inventory and impact assessment and whether these frameworks are valid and/or whether they can be modified for nano-evaluations. Method In order to do that, we reviewed the state-of-the-art literature on environmental impacts of nanomaterials and life cycle assessment studies on ENMs and nanoproducts. We evaluated the major characteristics and mechanisms under which nanomaterials affect the environment and whether these characteristics and mechanisms can be adequately addressed with current life cycle inventories and impact assessment practices. We also discuss whether the current data and knowledge accumulated around fate, transport, and toxicity of nanomaterials can be used to perform an interim evaluation while more data are being generated. Observations and recommendations We found that while there is plenty of literature available promoting LCA as a viable tool for ENMs and nanoproducts, there are only a handful of studies where at least some parts of life cycle were evaluated for nanoproducts or nanomaterial. None of the LCA studies on ENMs or nanoproducts that we came across assessed nano-specific fate, transport, and toxicity effects as part of their evaluation citing the lack of data as the primary reason. However, our literature review indicates that nano-LCA studies need not omit the assessment of nanomaterials’ human health and environmental impact due to incomplete data. There is some evidence that scalability may exist in certain types of nanomaterial, and traditional characterization can be applied even below 100 nm up to the scalability breakdown limits. For the size range where the scalability cannot be established, it may be more appropriate to explore empirical relationships, though possibly crude, between nanomaterial properties and their impact on human health and environment. Empirical relationships thus derived can serve as valid input for assessment until specific data points for nanomaterial fate, transport, and toxicity become available. Finally, where there is no quantitative data available, qualitative inferences may be drawn based on the known information of the nanomaterial and its potential release pathways. LCA of engineered nanomaterials (dpeaa)DE-He213 LCI of engineered nanomaterials (dpeaa)DE-He213 LCIA of engineered nanomaterials (dpeaa)DE-He213 Nanomaterial fate (dpeaa)DE-He213 Transport (dpeaa)DE-He213 Toxicity (dpeaa)DE-He213 Suh, Sangwon verfasserin aut Keller, Arturo F. verfasserin aut Enthalten in The international journal of life cycle assessment Berlin : Springer, 1996 17(2012), 3 vom: 11. Jan., Seite 295-303 (DE-627)313652961 (DE-600)2009386-X 1614-7502 nnns volume:17 year:2012 number:3 day:11 month:01 pages:295-303 https://dx.doi.org/10.1007/s11367-011-0368-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.33 ASE 85.15 ASE 85.35 ASE AR 17 2012 3 11 01 295-303 |
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10.1007/s11367-011-0368-5 doi (DE-627)SPR018929230 (SPR)s11367-011-0368-5-e DE-627 ger DE-627 rakwb eng 690 ASE 43.33 bkl 85.15 bkl 85.35 bkl Gavankar, Sheetal verfasserin aut Life cycle assessment at nanoscale: review and recommendations 2012 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The need for a systematic evaluation of the human and environmental impacts of engineered nanomaterials (ENMs) has been widely recognized, and a growing body of literature is available endorsing life cycle assessment (LCA) as a valid tool for the same. The purpose of this study is to evaluate how the nano-specific environmental assessments are being done within the existing framework of life cycle inventory and impact assessment and whether these frameworks are valid and/or whether they can be modified for nano-evaluations. Method In order to do that, we reviewed the state-of-the-art literature on environmental impacts of nanomaterials and life cycle assessment studies on ENMs and nanoproducts. We evaluated the major characteristics and mechanisms under which nanomaterials affect the environment and whether these characteristics and mechanisms can be adequately addressed with current life cycle inventories and impact assessment practices. We also discuss whether the current data and knowledge accumulated around fate, transport, and toxicity of nanomaterials can be used to perform an interim evaluation while more data are being generated. Observations and recommendations We found that while there is plenty of literature available promoting LCA as a viable tool for ENMs and nanoproducts, there are only a handful of studies where at least some parts of life cycle were evaluated for nanoproducts or nanomaterial. None of the LCA studies on ENMs or nanoproducts that we came across assessed nano-specific fate, transport, and toxicity effects as part of their evaluation citing the lack of data as the primary reason. However, our literature review indicates that nano-LCA studies need not omit the assessment of nanomaterials’ human health and environmental impact due to incomplete data. There is some evidence that scalability may exist in certain types of nanomaterial, and traditional characterization can be applied even below 100 nm up to the scalability breakdown limits. For the size range where the scalability cannot be established, it may be more appropriate to explore empirical relationships, though possibly crude, between nanomaterial properties and their impact on human health and environment. Empirical relationships thus derived can serve as valid input for assessment until specific data points for nanomaterial fate, transport, and toxicity become available. Finally, where there is no quantitative data available, qualitative inferences may be drawn based on the known information of the nanomaterial and its potential release pathways. LCA of engineered nanomaterials (dpeaa)DE-He213 LCI of engineered nanomaterials (dpeaa)DE-He213 LCIA of engineered nanomaterials (dpeaa)DE-He213 Nanomaterial fate (dpeaa)DE-He213 Transport (dpeaa)DE-He213 Toxicity (dpeaa)DE-He213 Suh, Sangwon verfasserin aut Keller, Arturo F. verfasserin aut Enthalten in The international journal of life cycle assessment Berlin : Springer, 1996 17(2012), 3 vom: 11. Jan., Seite 295-303 (DE-627)313652961 (DE-600)2009386-X 1614-7502 nnns volume:17 year:2012 number:3 day:11 month:01 pages:295-303 https://dx.doi.org/10.1007/s11367-011-0368-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.33 ASE 85.15 ASE 85.35 ASE AR 17 2012 3 11 01 295-303 |
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10.1007/s11367-011-0368-5 doi (DE-627)SPR018929230 (SPR)s11367-011-0368-5-e DE-627 ger DE-627 rakwb eng 690 ASE 43.33 bkl 85.15 bkl 85.35 bkl Gavankar, Sheetal verfasserin aut Life cycle assessment at nanoscale: review and recommendations 2012 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The need for a systematic evaluation of the human and environmental impacts of engineered nanomaterials (ENMs) has been widely recognized, and a growing body of literature is available endorsing life cycle assessment (LCA) as a valid tool for the same. The purpose of this study is to evaluate how the nano-specific environmental assessments are being done within the existing framework of life cycle inventory and impact assessment and whether these frameworks are valid and/or whether they can be modified for nano-evaluations. Method In order to do that, we reviewed the state-of-the-art literature on environmental impacts of nanomaterials and life cycle assessment studies on ENMs and nanoproducts. We evaluated the major characteristics and mechanisms under which nanomaterials affect the environment and whether these characteristics and mechanisms can be adequately addressed with current life cycle inventories and impact assessment practices. We also discuss whether the current data and knowledge accumulated around fate, transport, and toxicity of nanomaterials can be used to perform an interim evaluation while more data are being generated. Observations and recommendations We found that while there is plenty of literature available promoting LCA as a viable tool for ENMs and nanoproducts, there are only a handful of studies where at least some parts of life cycle were evaluated for nanoproducts or nanomaterial. None of the LCA studies on ENMs or nanoproducts that we came across assessed nano-specific fate, transport, and toxicity effects as part of their evaluation citing the lack of data as the primary reason. However, our literature review indicates that nano-LCA studies need not omit the assessment of nanomaterials’ human health and environmental impact due to incomplete data. There is some evidence that scalability may exist in certain types of nanomaterial, and traditional characterization can be applied even below 100 nm up to the scalability breakdown limits. For the size range where the scalability cannot be established, it may be more appropriate to explore empirical relationships, though possibly crude, between nanomaterial properties and their impact on human health and environment. Empirical relationships thus derived can serve as valid input for assessment until specific data points for nanomaterial fate, transport, and toxicity become available. Finally, where there is no quantitative data available, qualitative inferences may be drawn based on the known information of the nanomaterial and its potential release pathways. LCA of engineered nanomaterials (dpeaa)DE-He213 LCI of engineered nanomaterials (dpeaa)DE-He213 LCIA of engineered nanomaterials (dpeaa)DE-He213 Nanomaterial fate (dpeaa)DE-He213 Transport (dpeaa)DE-He213 Toxicity (dpeaa)DE-He213 Suh, Sangwon verfasserin aut Keller, Arturo F. verfasserin aut Enthalten in The international journal of life cycle assessment Berlin : Springer, 1996 17(2012), 3 vom: 11. Jan., Seite 295-303 (DE-627)313652961 (DE-600)2009386-X 1614-7502 nnns volume:17 year:2012 number:3 day:11 month:01 pages:295-303 https://dx.doi.org/10.1007/s11367-011-0368-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.33 ASE 85.15 ASE 85.35 ASE AR 17 2012 3 11 01 295-303 |
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The purpose of this study is to evaluate how the nano-specific environmental assessments are being done within the existing framework of life cycle inventory and impact assessment and whether these frameworks are valid and/or whether they can be modified for nano-evaluations. Method In order to do that, we reviewed the state-of-the-art literature on environmental impacts of nanomaterials and life cycle assessment studies on ENMs and nanoproducts. We evaluated the major characteristics and mechanisms under which nanomaterials affect the environment and whether these characteristics and mechanisms can be adequately addressed with current life cycle inventories and impact assessment practices. We also discuss whether the current data and knowledge accumulated around fate, transport, and toxicity of nanomaterials can be used to perform an interim evaluation while more data are being generated. Observations and recommendations We found that while there is plenty of literature available promoting LCA as a viable tool for ENMs and nanoproducts, there are only a handful of studies where at least some parts of life cycle were evaluated for nanoproducts or nanomaterial. None of the LCA studies on ENMs or nanoproducts that we came across assessed nano-specific fate, transport, and toxicity effects as part of their evaluation citing the lack of data as the primary reason. However, our literature review indicates that nano-LCA studies need not omit the assessment of nanomaterials’ human health and environmental impact due to incomplete data. There is some evidence that scalability may exist in certain types of nanomaterial, and traditional characterization can be applied even below 100 nm up to the scalability breakdown limits. For the size range where the scalability cannot be established, it may be more appropriate to explore empirical relationships, though possibly crude, between nanomaterial properties and their impact on human health and environment. Empirical relationships thus derived can serve as valid input for assessment until specific data points for nanomaterial fate, transport, and toxicity become available. 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Gavankar, Sheetal Suh, Sangwon Keller, Arturo F. |
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Gavankar, Sheetal |
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life cycle assessment at nanoscale: review and recommendations |
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Life cycle assessment at nanoscale: review and recommendations |
| abstract |
Purpose The need for a systematic evaluation of the human and environmental impacts of engineered nanomaterials (ENMs) has been widely recognized, and a growing body of literature is available endorsing life cycle assessment (LCA) as a valid tool for the same. The purpose of this study is to evaluate how the nano-specific environmental assessments are being done within the existing framework of life cycle inventory and impact assessment and whether these frameworks are valid and/or whether they can be modified for nano-evaluations. Method In order to do that, we reviewed the state-of-the-art literature on environmental impacts of nanomaterials and life cycle assessment studies on ENMs and nanoproducts. We evaluated the major characteristics and mechanisms under which nanomaterials affect the environment and whether these characteristics and mechanisms can be adequately addressed with current life cycle inventories and impact assessment practices. We also discuss whether the current data and knowledge accumulated around fate, transport, and toxicity of nanomaterials can be used to perform an interim evaluation while more data are being generated. Observations and recommendations We found that while there is plenty of literature available promoting LCA as a viable tool for ENMs and nanoproducts, there are only a handful of studies where at least some parts of life cycle were evaluated for nanoproducts or nanomaterial. None of the LCA studies on ENMs or nanoproducts that we came across assessed nano-specific fate, transport, and toxicity effects as part of their evaluation citing the lack of data as the primary reason. However, our literature review indicates that nano-LCA studies need not omit the assessment of nanomaterials’ human health and environmental impact due to incomplete data. There is some evidence that scalability may exist in certain types of nanomaterial, and traditional characterization can be applied even below 100 nm up to the scalability breakdown limits. For the size range where the scalability cannot be established, it may be more appropriate to explore empirical relationships, though possibly crude, between nanomaterial properties and their impact on human health and environment. Empirical relationships thus derived can serve as valid input for assessment until specific data points for nanomaterial fate, transport, and toxicity become available. Finally, where there is no quantitative data available, qualitative inferences may be drawn based on the known information of the nanomaterial and its potential release pathways. |
| abstractGer |
Purpose The need for a systematic evaluation of the human and environmental impacts of engineered nanomaterials (ENMs) has been widely recognized, and a growing body of literature is available endorsing life cycle assessment (LCA) as a valid tool for the same. The purpose of this study is to evaluate how the nano-specific environmental assessments are being done within the existing framework of life cycle inventory and impact assessment and whether these frameworks are valid and/or whether they can be modified for nano-evaluations. Method In order to do that, we reviewed the state-of-the-art literature on environmental impacts of nanomaterials and life cycle assessment studies on ENMs and nanoproducts. We evaluated the major characteristics and mechanisms under which nanomaterials affect the environment and whether these characteristics and mechanisms can be adequately addressed with current life cycle inventories and impact assessment practices. We also discuss whether the current data and knowledge accumulated around fate, transport, and toxicity of nanomaterials can be used to perform an interim evaluation while more data are being generated. Observations and recommendations We found that while there is plenty of literature available promoting LCA as a viable tool for ENMs and nanoproducts, there are only a handful of studies where at least some parts of life cycle were evaluated for nanoproducts or nanomaterial. None of the LCA studies on ENMs or nanoproducts that we came across assessed nano-specific fate, transport, and toxicity effects as part of their evaluation citing the lack of data as the primary reason. However, our literature review indicates that nano-LCA studies need not omit the assessment of nanomaterials’ human health and environmental impact due to incomplete data. There is some evidence that scalability may exist in certain types of nanomaterial, and traditional characterization can be applied even below 100 nm up to the scalability breakdown limits. For the size range where the scalability cannot be established, it may be more appropriate to explore empirical relationships, though possibly crude, between nanomaterial properties and their impact on human health and environment. Empirical relationships thus derived can serve as valid input for assessment until specific data points for nanomaterial fate, transport, and toxicity become available. Finally, where there is no quantitative data available, qualitative inferences may be drawn based on the known information of the nanomaterial and its potential release pathways. |
| abstract_unstemmed |
Purpose The need for a systematic evaluation of the human and environmental impacts of engineered nanomaterials (ENMs) has been widely recognized, and a growing body of literature is available endorsing life cycle assessment (LCA) as a valid tool for the same. The purpose of this study is to evaluate how the nano-specific environmental assessments are being done within the existing framework of life cycle inventory and impact assessment and whether these frameworks are valid and/or whether they can be modified for nano-evaluations. Method In order to do that, we reviewed the state-of-the-art literature on environmental impacts of nanomaterials and life cycle assessment studies on ENMs and nanoproducts. We evaluated the major characteristics and mechanisms under which nanomaterials affect the environment and whether these characteristics and mechanisms can be adequately addressed with current life cycle inventories and impact assessment practices. We also discuss whether the current data and knowledge accumulated around fate, transport, and toxicity of nanomaterials can be used to perform an interim evaluation while more data are being generated. Observations and recommendations We found that while there is plenty of literature available promoting LCA as a viable tool for ENMs and nanoproducts, there are only a handful of studies where at least some parts of life cycle were evaluated for nanoproducts or nanomaterial. None of the LCA studies on ENMs or nanoproducts that we came across assessed nano-specific fate, transport, and toxicity effects as part of their evaluation citing the lack of data as the primary reason. However, our literature review indicates that nano-LCA studies need not omit the assessment of nanomaterials’ human health and environmental impact due to incomplete data. There is some evidence that scalability may exist in certain types of nanomaterial, and traditional characterization can be applied even below 100 nm up to the scalability breakdown limits. For the size range where the scalability cannot be established, it may be more appropriate to explore empirical relationships, though possibly crude, between nanomaterial properties and their impact on human health and environment. Empirical relationships thus derived can serve as valid input for assessment until specific data points for nanomaterial fate, transport, and toxicity become available. Finally, where there is no quantitative data available, qualitative inferences may be drawn based on the known information of the nanomaterial and its potential release pathways. |
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Life cycle assessment at nanoscale: review and recommendations |
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| score |
7.3983355 |