Dataset | Database | DQI | Score | Short justification of DQI | DQR |
---|---|---|---|---|---|
Electricity From nuclear power (FR) | ELCD | TeR | 1 | Modelled as the French technology mix | 1.83 |
GR | 2 | Some activities of milling and reprocessing refers to US data | |||
TiR | 3 | Some references are 20 years older than the ref. year (2009) | |||
C | 1 | 100% of impact categories and 100% of reference flows covered | |||
P | 2 | Relevant flows measured, other flows taken from literature | |||
M | 2 | EoL of intermediate activities is missing | |||
Ecoinvent | TeR | 2 | Some data extrapolated from Swiss power plants | 1.67 | |
GR | 2 | Infrastructure data from Swiss plants, only 1 uranium supplier | |||
TiR | 2 | Ref. year 2002, relevant data are more updated than ELCD | |||
C | 1 | 100% of impact categories and 100% of reference flows covered | |||
P | 2 | Relevant flows measured, other flows taken from literature | |||
M | 1 | EoL and allocation also for sub-processes | |||
GEMIS | TeR | 2 | Referred to French representative plants but not as a mix | 3.08 | |
GR | 4 | Only the modeling of enrichment is correct | |||
TiR | 2-3 | (depending on plant) literature comes from 5–15 years before | |||
C | 2 | 75% of impact categories, 90% of flows covered | |||
P | 4 | Literature data and auto-estimated data | |||
M | 4 | EoL not modeled, not including infrastructures. | |||
E3 | TeR | 4 | Considering a process scale instead of real plant | 4.00 | |
GR | 4 | Only the modeling of enrichment is correct | |||
TiR | 3 | Reference year 2000, data from 1994-99 | |||
C | 4 | Less than 50% impact categories, 90% flows covered | |||
P | 4 | Literature data and auto-estimated data | |||
M | 5 | Cradle to gate system, EoL and infrastructure lacking | |||
Diesel mix (EU27) | ELCD | TeR | 1 | Relevant primary and secondary data referred to EU27 | 1.08 |
GR | 1 | Very good modeling of EU27 share and market relevance | |||
TiR | 1 | Ref year 2009, data from 2007 to 2009 | |||
C | 1 | 100% of impact categories, 96% of flows covered | |||
P | 1-2 | Some data are calculated basing on technical descriptions | |||
M | 1 | Cradle to grave process, EoL and infrastructure included | |||
Ecoinvent | TeR | 2 | Some transport distances refers to Swiss refineries | 1.75 | |
GR | 2 | Few countries not included | |||
TiR | 1-2 | Ref year 2000, some data from ‘80s | |||
C | 1 | 100% of impact categories and 100% of reference flows covered | |||
P | 2 | Some oil extraction data from Africa are roughly estimated | |||
M | 2 | EoL not modelled, infrastructure included | |||
GEMIS | TeR | 3 | Modelled by a generic plant, default distance values | 3.50 | |
GR | 5 | Not referred to any specific country | |||
TiR | 4 | Ref year 2000, data from 1985-95 | |||
C | 2 | 75% of impact categories, 90% of flows covered | |||
P | 4 | Estimated data from literature, assumptions not disclosed | |||
M | 3 | EoL not comprised, Allocation not specified | |||
E3 | TeR | 2 | Modelled from CONCAWE report assuming oil from middle east | 2.67 | |
GR | 3 | Extraction only from mid. east, representativeness of EU refinery system is not explained | |||
TiR | 2 | Ref. year 2010, data coming from CONCAWE (1996–2007) | |||
C | 4 | Less than 50% of impact categories, 90% of flows covered | |||
P | 2 | No info about emission factors | |||
M | 3 | Cradle to gate system, EoL not included. |