Key Data Set Information | |
Location | CN |
Reference year | 2013 |
Name |
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Use advice for data set | Users of this Life Cycle Assessment (LCA) data set should note that the input-output of Process E is derived from averaged literature review data representing a 'cradle-to-grave' approach within the time frame of 2013-2017. The data excludes considerations of plastic and metal casing recycling or treatment, as well as labor and factory construction costs and their environmental impact. Additionally, users should exercise caution when applying this EU-based data in the Chinese context, as it may not completely align with the industry-specific conditions in China. Modifications using official Chinese data, industry reports, and information from trade associations have been estimated to reflect the data from Chinese stakeholders better. For timeliness, reference the data from the most recent four-year average period available, specifically 2013-2016. Functional unit (FU) reference is based on 100 kg of typical LIB electrode material. |
Technical purpose of product or process | The hydrometallurgical organic acid leaching process (Process E) uses weak acids such as acetic acid and citric acid along with a reducing agent as the leaching solution. The weak acid selectively leaches valuable metals by reacting with the active materials of the positive electrode while not affecting the aluminum foil collector. This allows for selective recovery and reprocessing of the electrode materials by adjusting the pH and adding metal salts to cause co-precipitation of the valuable metals. This process is applicable in the battery recycling industry, particularly for the regeneration of Lithium-Ion Battery (LIB) electrode materials. |
Classification |
Class name
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Hierarchy level
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General comment on data set | Weak acid (e.g. acetic acid, citric acid, etc.) and reducing agent are used as leaching agent, and the weak acid can react with positive electrode active material without reacting with the aluminum foil of collector, so as to realize selective leaching of valuable metal, and the product can realize electrode active material reproduction by adjusting pH, adding metal salt and so on, so as to cause co-precipitation of valuable metal. |
Copyright | No |
Owner of data set | |
Quantitative reference | |
Reference flow(s) |
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Functional Unit | FU is a typical type of LIB electrode material of 100 kg |
Time representativeness | |
Data set valid until | 2017 |
Time representativeness description | Data source: 2013-2017 |
Technological representativeness | |
Flow diagram(s) or picture(s) |
LCI method and allocation | |||||
Type of data set | Unit process, single operation | ||||
Deviation from LCI method principle / explanations | None | ||||
Deviation from modelling constants / explanations | None | ||||
Data sources, treatment and representativeness | |||||
Deviation from data cut-off and completeness principles / explanations | None | ||||
Data selection and combination principles | The input-output of the process comes from the average results of the data reported in the literature review, reflecting the representative process from "tomb" to "cradle". This study does not consider the recycling or treatment of plastic and metal shells, and labor costs, factory construction costs, and their impact on the environment are also not included in this analysis. | ||||
Deviation from data selection and combination principles / explanations | None | ||||
Data treatment and extrapolations principles | It is worth noting that the EU's data is not specific to a specific industry, and some import and export data and recycling information are not suitable for China's situation. Therefore, the improved CRMs evaluation method also combines official Chinese data, literature reports, and data from other interest groups such as trade/industry associations to conduct the best estimation of data from major LIB manufacturers, recycling companies, official management agencies in China, and other stakeholders. In terms of data timeliness, the reference period used in the evaluation of CRMs is based on the latest 4-year average (i.e. 2013-2016). | ||||
Deviation from data treatment and extrapolations principles / explanations | None | ||||
Data source(s) used for this data set | |||||
Completeness | |||||
Completeness of product model | No statement | ||||
Validation | |||||
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Data generator | |
Data set generator / modeller | |
Data entry by | |
Time stamp (last saved) | 2024-02-04T12:52:34+08:00 |
Publication and ownership | |
UUID | 256a84ce-b47a-493b-8ade-554b70e9cc6c |
Date of last revision | 2024-05-13T14:56:16.287482+08:00 |
Data set version | 01.00.005 |
Permanent data set URI | https://lcadata.tiangong.world/showProcess.xhtml?uuid=256a84ce-b47a-493b-8ade-554b70e9cc6c&version=01.00.000&stock=TianGong |
Owner of data set | |
Copyright | No |
License type | Free of charge for all users and uses |
Inputs
Type of flow | Classification | Flow | Location | Mean amount | Resulting amount | Minimum amount | Maximum amount | ||
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Product flow | Materials production / Other materials | 100.0 kg | 100.0 kg | ||||||
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Product flow | Materials production / Organic chemicals | 93.3 kg | 93.3 kg | ||||||
Product flow | Materials production / Inorganic chemicals | 17.0 kg | 17.0 kg | ||||||
Product flow | Materials production / Inorganic chemicals | 3.0 kg | 3.0 kg | ||||||
Product flow | Materials production / Inorganic chemicals | 10.6 kg | 10.6 kg | ||||||
Elementary flow | Resources / Resources from water / Renewable material resources from water | 380.0 m3 | 380.0 m3 | ||||||
Product flow | Materials production / Other mineralic materials | 1.4 kg | 1.4 kg | ||||||
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Product flow | Energy carriers and technologies / Electricity | 64.08 MJ | 64.08 MJ |
Outputs
Type of flow | Classification | Flow | Location | Mean amount | Resulting amount | Minimum amount | Maximum amount | ||
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Product flow | Materials production / Inorganic chemicals | 10.5 kg | 10.5 kg | ||||||
Product flow | Materials production / Inorganic chemicals | 17.6 kg | 17.6 kg | ||||||
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Product flow | Materials production / Other materials | 5.4 kg | 5.4 kg | ||||||
Product flow | Materials production / Other materials | 14.0 kg | 14.0 kg | ||||||
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Product flow | Materials production / Other materials | 15.0 kg | 15.0 kg | ||||||
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Product flow | Materials production / Other materials | 12.0 kg | 12.0 kg | ||||||
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Product flow | Materials production / Other materials | 10.0 kg | 10.0 kg | ||||||
Waste flow | Wastes | 4.8 kg | 4.8 kg | ||||||
Elementary flow | Emissions / Emissions to air / Emissions to air, unspecified | 9.0 kg | 9.0 kg | ||||||
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Product flow | End-of-life treatment / Waste water treatment | 360.0 kg | 360.0 kg |