Characterisation factors → EF 3.1
Land use
Soil quality index
- Method
- EF 3.1
- Reference unit
- SQI
- Protects
- Ecosystem Quality
Land occupied or transformed, weighted by what that does to the soil's capacity to support life.
consensus-flow-list
36,476
factors over 224 flows,
36,341 of them non-zero
European Commission — JRC
36,423
factors over 171 flows,
36,288 of them non-zero
GreenDelta
16,224
factors over 121 flows,
16,223 of them non-zero
ecoinvent Centre
150
factors over 150 flows,
150 of them non-zero
Compare two of these implementations — only the rows where they state different numbers.
Factors
41,910One row per flow and place. Published as is what this list did with the row: agreed where more than one implementation stated the same number, sole where only one spoke, and nothing at all where the disagreement went to a queue instead.
| Flow | Place | consensus-flow-list | European Commission — JRC | GreenDelta | ecoinvent Centre | Published as |
|---|---|---|---|---|---|---|
|
From construction site
Land Use → Transformation
|
VU | -10,550 | -10,550 | — | — | sole |
|
From traffic area, road network
Land Use → Transformation
|
GE | -10,547 | -10,547 | -10,547 | — | sole |
|
To traffic area, road network
Land Use → Transformation
|
GE | 10,547 | 10,547 | 10,547 | — | sole |
|
To mineral extraction site
Land Use → Transformation
|
PA | 10,543 | 10,543 | 10,543 | — | sole |
|
To construction site
Land Use → Transformation
|
PA | 10,543 | 10,543 | — | — | sole |
|
From mineral extraction site
Land Use → Transformation
|
PA | -10,543 | -10,543 | -10,543 | — | sole |
|
From construction site
Land Use → Transformation
|
PA | -10,543 | -10,543 | — | — | sole |
|
From dump site
Land Use → Transformation
|
AD | -10,535 | -10,535 | — | — | sole |
|
From dump site, slag compartment
Land Use → Transformation
|
AD | — | — | -10,535 | — | not published |
|
To dump site, slag compartment
Land Use → Transformation
|
AD | — | — | 10,535 | — | not published |
|
To dump site, sanitary landfill
Land Use → Transformation
|
AD | — | — | 10,535 | — | not published |
|
From dump site, inert material landfill
Land Use → Transformation
|
AD | — | — | -10,535 | — | not published |
|
From dump site, residual material landfill
Land Use → Transformation
|
AD | — | — | -10,535 | — | not published |
|
To dump site
Land Use → Transformation
|
AD | 10,535 | 10,535 | 10,535 | — | sole |
|
From dump site, sanitary landfill
Land Use → Transformation
|
AD | — | — | -10,535 | — | not published |
|
To dump site, residual material landfill
Land Use → Transformation
|
AD | — | — | 10,535 | — | not published |
|
To dump site, benthic
Land Use → Transformation
|
AD | — | — | 10,535 | — | not published |
|
To dump site, inert material landfill
Land Use → Transformation
|
AD | — | — | 10,535 | — | not published |
|
From urban, continuously built
Land Use → Transformation
|
GG | -10,520 | -10,520 | -10,520 | — | sole |
|
To urban, continuously built
Land Use → Transformation
|
GG | 10,520 | 10,520 | 10,520 | — | sole |
|
To mineral extraction site
Land Use → Transformation
|
AT | 10,511 | 10,511 | 10,511 | — | sole |
|
To construction site
Land Use → Transformation
|
AT | 10,511 | 10,511 | — | — | sole |
|
From mineral extraction site
Land Use → Transformation
|
AT | -10,511 | -10,511 | -10,511 | — | sole |
|
From construction site
Land Use → Transformation
|
AT | -10,511 | -10,511 | — | — | sole |
|
From urban, continuously built
Land Use → Transformation
|
IS | -10,501 | -10,501 | -10,501 | — | sole |
|
From urban
Land Use → Transformation
|
IS | -10,501 | -10,501 | — | — | sole |
|
To urban
Land Use → Transformation
|
IS | 10,501 | 10,501 | — | — | sole |
|
To urban, continuously built
Land Use → Transformation
|
IS | 10,501 | 10,501 | 10,501 | — | sole |
|
From dump site
Land Use → Transformation
|
SI | -10,497 | -10,497 | — | — | sole |
|
From dump site, slag compartment
Land Use → Transformation
|
SI | — | — | -10,497 | — | not published |
|
To dump site, slag compartment
Land Use → Transformation
|
SI | — | — | 10,497 | — | not published |
|
To dump site, sanitary landfill
Land Use → Transformation
|
SI | — | — | 10,497 | — | not published |
|
From dump site, inert material landfill
Land Use → Transformation
|
SI | — | — | -10,497 | — | not published |
|
From dump site, residual material landfill
Land Use → Transformation
|
SI | — | — | -10,497 | — | not published |
|
To dump site
Land Use → Transformation
|
SI | 10,497 | 10,497 | 10,497 | — | sole |
|
From dump site, sanitary landfill
Land Use → Transformation
|
SI | — | — | -10,497 | — | not published |
|
To dump site, residual material landfill
Land Use → Transformation
|
SI | — | — | 10,497 | — | not published |
|
To dump site, benthic
Land Use → Transformation
|
SI | — | — | 10,497 | — | not published |
|
To dump site, inert material landfill
Land Use → Transformation
|
SI | — | — | 10,497 | — | not published |
|
To traffic area, rail and road embankment
Land Use → Transformation
|
SI | 10,494 | 10,494 | 10,494 | — | sole |
|
From traffic area, rail and road embankment
Land Use → Transformation
|
SI | -10,494 | -10,494 | -10,494 | — | sole |
|
From traffic area, road network
Land Use → Transformation
|
IS | -10,490 | -10,490 | -10,490 | — | sole |
|
To traffic area, road network
Land Use → Transformation
|
IS | 10,490 | 10,490 | 10,490 | — | sole |
|
To artificial area
Land Use → Transformation
|
IS | 10,473 | 10,473 | — | — | sole |
|
From artificial area
Land Use → Transformation
|
IS | -10,473 | -10,473 | — | — | sole |
|
To mineral extraction site
Land Use → Transformation
|
DM | 10,470 | 10,470 | 10,470 | — | sole |
|
To construction site
Land Use → Transformation
|
DM | 10,470 | 10,470 | — | — | sole |
|
From mineral extraction site
Land Use → Transformation
|
DM | -10,470 | -10,470 | -10,470 | — | sole |
|
From construction site
Land Use → Transformation
|
DM | -10,470 | -10,470 | — | — | sole |
|
From industrial area
Land Use → Transformation
|
JE | -10,463 | -10,463 | -10,463 | — | sole |
Where two of these implementations differ, only the rows they state different numbers for — or this category in the whole-method difference report.