_images/large.png

User guide

This user guide will help you navigate the inner workings of premise.

In a nutshell

Purpose

premise enables the alignment of life cycle inventories within the ecoinvent 3.6-3.9.1 database, using either a “cut-off” or “consequential” system model, to match the output results of Integrated Assessment Models (IAMs) such as REMIND or IMAGE. This allows for the creation of life cycle inventory databases under future policy scenarios for any year between 2005 and 2100.

Note

The ecoinvent database is not included in this package. You need to have a valid license for ecoinvent 3.6-3.9.1 to use premise. Also, please read carefully ecoinvent’s EULA before using premise.

Publication

The methodology behind premise is described in the following publication:

R. Sacchi, T. Terlouw, K. Siala, A. Dirnaichner, C. Bauer, B. Cox, C. Mutel, V. Daioglou, G. Luderer, PRospective EnvironMental Impact asSEment (premise): A streamlined approach to producing databases for prospective life cycle assessment using integrated assessment models, Renewable and Sustainable Energy Reviews, 2022, https://doi.org/10.1016/j.rser.2022.112311.

Note

If you use premise in your research, please cite the above publication.

Workflow

_images/main_workflow.png

As illustrated in the workflow diagram above, premise follows an Extract, Transform, Load (ETL) process:

Extract the ecoinvent database from a Brightway project or from ecospold2 files. Expand the database by adding additional inventories for future production pathways for certain commodities, such as electricity, steel, cement, etc. Modify the ecoinvent database, focusing primarily on process efficiency improvements and market adjustments. Load the updated database back into a Brightway project or export it as a set of CSV files, such as Simapro CSV files.

Default IAM scenarios

Provided a decryption key (ask the maintainers), the following IAM scenarios are available when installing premise:

SSP/RCP scenario

GMST increase by 2100

Society/economy trend

Climate policy

REMIND

IMAGE

SSP1-None

2.3-2.8 °C

Optimistic trends for human develop. and economy, driven by sustainable practices.

None

SSP1-Base

SSP1-Base

SSP1-None

~2.2 °C

Optimistic trends for human develop. and economy, driven by sustainable practices.

National Policies Implemented (NPI).

SSP1-NPi

SSP1-None

~1.9 °C

Optimistic trends for human develop. and economy, driven by sustainable practices.

Nationally Determined Contributions (NDCs).

SSP1-NDC

SSP1-RCP2.6

~1.7 °C

Optimistic trends for human develop. and economy, driven by sustainable practices.

Paris Agreement objective.

SSP1-PkBudg1150

SSP1-RCP1.9

~1.3 °C

Optimistic trends for human develop. and economy, driven by sustainable practices.

Paris Agreement objective.

SSP1-PkBudg500

SSP2-None

~3.5 °C

Extrapolation from historical developments.

None (eq. to RCP6)

SSP2-Base

SSP2-Base

SSP2-None

~3.3 °C

Extrapolation from historical developments.

National Policies Implemented (NPI).

SSP2-NPi

SSP2-None

~2.5 °C

Extrapolation from historical developments.

Nationally Determined Contributions (NDCs).

SSP2-NDC

SSP2-RCP2.6

1.6-1.8 °C

Extrapolation from historical developments.

Paris Agreement objective.

SSP2-PkBudg1150

SSP2-RCP26

SSP2-RCP1.9

1.2-1.4 °C

Extrapolation from historical developments.

Paris Agreement objective.

SSP2-PkBudg500

SSP2-RCP19

SSP5-None

~4.5 °C

Optimistic trends for human develop. and economy, driven by fossil fuels.

None

SSP5-Base

SSP5-None

~4.0 °C

Optimistic trends for human develop. and economy, driven by fossil fuels.

National Policies Implemented (NPI).

SSP5-NPi

SSP5-None

~3.0 °C

Optimistic trends for human develop. and economy, driven by fossil fuels.

Nationally Determined Contributions (NDCs).

SSP5-NDC

SSP5-RCP2.6

~1.7 °C

Optimistic trends for human develop. and economy, driven by fossil fuels.

Paris Agreement objective.

SSP5-PkBudg1150

SSP5-RCP1.9

~1.0 °C

Optimistic trends for human develop. and economy, driven by fossil fuels.

Paris Agreement objective.

SSP5-PkBudg500

CarbonBrief wrote a good article explaining the meaning of the SSP/RCP system.

Additionally, we provided a summary of the main characteristics of each scenario here.

You can however use any other scenario files generated by REMIND or IMAGE. If you wish to use an IAM file which has not been generated by either of these two models, you should refer to the Mapping section.

Requirements

  • Python language interpreter >=3.9

  • License for ecoinvent 3

  • brightway2 (optional)

How to install this package?

Two options:

A development version with the latest advancements (but with the risks of unseen bugs), is available on Anaconda Cloud:

conda install -c romainsacchi premise

For a more stable and proven version, from Pypi:

pip install premise

This will install the package and the required dependencies.

How to use it?

Examples notebook

This notebook will show you everything you need to know to use premise.

Main contributors

EXTRACT

The EXTRACT phase consists of the following steps:

  • Extraction and cleaning of the ecoinvent database

  • Import and cleaning of additional inventories

  • Import and cleaning of user-provided inventories (optional)

  • Caching, if these database and inventories are imported for the first time

  • Loading of IAM data

Current IAM scenarios

premise includes several Integrated Assessment Model (IAM) scenarios, but you can also use other scenarios. In premise, scenarios are defined by their Shared Socio-economic Pathway (SSP), a climate trajectory—often represented by a Representative Concentration Pathway (RCP)—and a year (e.g., SSP1, Base, 2035).

SSP/RCP scenario

GMST increase by 2100

Society/economy trend

Climate policy

REMIND

IMAGE

SSP1-None

2.3-2.8 °C

Optimistic trends for human develop. and economy, driven by sustainable practices.

None

SSP1-Base

SSP1-Base

SSP1-None

~2.2 °C

Optimistic trends for human develop. and economy, driven by sustainable practices.

National Policies Implemented (NPI).

SSP1-NPi

SSP1-None

~1.9 °C

Optimistic trends for human develop. and economy, driven by sustainable practices.

Nationally Determined Contributions (NDCs).

SSP1-NDC

SSP1-RCP2.6

~1.7 °C

Optimistic trends for human develop. and economy, driven by sustainable practices.

Paris Agreement objective.

SSP1-PkBudg1150

SSP1-RCP1.9

~1.3 °C

Optimistic trends for human develop. and economy, driven by sustainable practices.

Paris Agreement objective.

SSP1-PkBudg500

SSP2-None

~3.5 °C

Extrapolation from historical developments.

None (eq. to RCP6)

SSP2-Base

SSP2-Base

SSP2-None

~3.3 °C

Extrapolation from historical developments.

National Policies Implemented (NPI).

SSP2-NPi

SSP2-None

~2.5 °C

Extrapolation from historical developments.

Nationally Determined Contributions (NDCs).

SSP2-NDC

SSP2-RCP2.6

1.6-1.8 °C

Extrapolation from historical developments.

Paris Agreement objective.

SSP2-PkBudg1150

SSP2-RCP26

SSP2-RCP1.9

1.2-1.4 °C

Extrapolation from historical developments.

Paris Agreement objective.

SSP2-PkBudg500

SSP2-RCP19

SSP5-None

~4.5 °C

Optimistic trends for human develop. and economy, driven by fossil fuels.

None

SSP5-Base

SSP5-None

~4.0 °C

Optimistic trends for human develop. and economy, driven by fossil fuels.

National Policies Implemented (NPI).

SSP5-NPi

SSP5-None

~3.0 °C

Optimistic trends for human develop. and economy, driven by fossil fuels.

Nationally Determined Contributions (NDCs).

SSP5-NDC

SSP5-RCP2.6

~1.7 °C

Optimistic trends for human develop. and economy, driven by fossil fuels.

Paris Agreement objective.

SSP5-PkBudg1150

SSP5-RCP1.9

~1.0 °C

Optimistic trends for human develop. and economy, driven by fossil fuels.

Paris Agreement objective.

SSP5-PkBudg500

Note

A summary report of the main variables of the scenarios selected is generated automatically after each database export. There is also an online dashboard. You can also generate it manually:

Supported versions of ecoinvent

premise currently works with the following ecoinvent database versions:

  • v.3.5, cut-off

  • v.3.6, cut-off

  • v.3.7, cut-off

  • v.3.7.1, cut-off

  • v.3.8, cut-off and consequential

  • v.3.9/3.9.1, cut-off and consequential

Supported sources of ecoinvent

premise can extract the ecoinvent database from:

  • a brightway2 project that contains the ecoinvent database

  • ecosposld2 files, that can be downloaded from the ecoinvent website

Note

The ecoinvent database is not included in premise. You need to have a valid license to download and use it. Also, please read carefully ecoinvent’s EULA before using premise.

From a brightway2 project

To extract from an ecoinvent database located in a brightway2 project, simply indicate the database name in source_db and its version in source_version:

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
      scenarios=[
              {"model":"remind", "pathway":"SSP2-Base", "year":2028}
          ],
      source_db="ecoinvent 3.7 cutoff", # <-- this is NEW.
      source_version="3.7.1", # <-- this is NEW
      key='xxxxxxxxxxxxxxxxxxxxxxxxx',
      use_multiprocessing=True, # True by default, set to False if multiprocessing is causing troubles
      keep_uncertainty_data=False # False by default, set to True if you want to keep ecoinvent's uncertainty data
  )

Note that a cache of the database will be created the first time and store in the library folder. Any subsequent creation of databases using the same ecoinvent version will no longer require this extraction step.

If you wish to clear that cache folder, do:

from premise import *

clear_cache()

Note

It is recommended to restart your notebook once the data has been cached for the first time, so that the remaining steps can be performed using the cached data (much faster).

From ecospold2 files

To extract from a set of ecospold2 files, you need to point to the location of those files in source_file_path, as well as indicate the database format in source_type:

from premise import *

ndb = NewDatabase(
    scenarios = [
        {"model":"remind", "pathway":"SSP2-Base", "year":2028}
                ],
    source_type="ecospold", # <--- this is NEW
    source_file_path=r"C:\file\path\to\ecoinvent 3.5_cutoff_ecoSpold02\datasets", # <-- this is NEW
    source_version="3.5",
)

Import of additional inventories

After the ecoinvent database is extracted and checked, a number of additional inventories are imported, regardless of the year of scenario that is being considered.

Power generation

A number of datasets relating to power generation not originally present in ecoinvent are imported. The next sub-sections lists such datasets.

Power plants with CCS

Datasets for power generation with Carbon Capture and Storage (CCS) are imported. They originate from Volkart et al. 2013, and can be consulted here: LCI_Power_generation. An exception to this are the inventories for biomass-based integrated gasification combined cycle power plants (BIGCCS), which are from Briones-Hidrovo et al, 2020.

The table below lists the names of the new activities (only production datasets are shown).

Power generation with CCS (activities list)

location

electricity production, at power plant/hard coal, IGCC, no CCS

RER

electricity production, at power plant/hard coal, PC, no CCS

RER

electricity production, at power plant/hard coal, oxy, pipeline 200km, storage 1000m

RER

electricity production, at power plant/hard coal, oxy, pipeline 400km, storage 3000m

RER

electricity production, at power plant/hard coal, post, pipeline 200km, storage 1000m

RER

electricity production, at power plant/hard coal, post, pipeline 400km, storage 1000m

RER

electricity production, at power plant/hard coal, post, pipeline 400km, storage 3000m

RER

electricity production, at power plant/hard coal, pre, pipeline 200km, storage 1000m

RER

electricity production, at power plant/hard coal, pre, pipeline 400km, storage 3000m

RER

electricity production, at power plant/lignite, IGCC, no CCS

RER

electricity production, at power plant/lignite, PC, no CCS

RER

electricity production, at power plant/lignite, oxy, pipeline 200km, storage 1000m

RER

electricity production, at power plant/lignite, oxy, pipeline 400km, storage 3000m

RER

electricity production, at power plant/lignite, post, pipeline 200km, storage 1000m

RER

electricity production, at power plant/lignite, post, pipeline 400km, storage 3000m

RER

electricity production, at power plant/lignite, pre, pipeline 200km, storage 1000m

RER

electricity production, at power plant/lignite, pre, pipeline 400km, storage 3000m

RER

electricity production, at power plant/natural gas, ATR H2-CC, no CCS

RER

electricity production, at power plant/natural gas, NGCC, no CCS/kWh

RER

electricity production, at power plant/natural gas, post, pipeline 200km, storage 1000m

RER

electricity production, at power plant/natural gas, post, pipeline 400km, storage 1000m

RER

electricity production, at power plant/natural gas, post, pipeline 400km, storage 3000m

RER

electricity production, at power plant/natural gas, pre, pipeline 200km, storage 1000m

RER

electricity production, at power plant/natural gas, pre, pipeline 400km, storage 3000m

RER

electricity production, at wood burning power plant 20 MW, truck 25km, no CCS

RER

electricity production, at wood burning power plant 20 MW, truck 25km, post, pipeline 200km, storage 1000m

RER

electricity production, at wood burning power plant 20 MW, truck 25km, post, pipeline 400km, storage 3000m

RER

Natural gas

Updated inventories relating to natural gas extraction and distribution are imported to substitute some of the original ecoinvent dataset. These datasets originate from ESU Services and come with a report, and can be consulted here: LCI_Oil_NG.

They have been adapted to a brightway2-compatible format. These new inventories have, among other things, higher methane slip emissions along the natural gas supply chain, especially at extraction.

Original dataset

Replaced by

natural gas production (natural gas, high pressure), DE

natural gas, at production (natural gas, high pressure), DE

natural gas production (natural gas, high pressure), DZ

natural gas, at production (natural gas, high pressure), DZ

natural gas production (natural gas, high pressure), US

natural gas, at production (natural gas, high pressure), US

natural gas production (natural gas, high pressure), RU

natural gas, at production (natural gas, high pressure), RU

petroleum and gas production, GB

natural gas, at production (natural gas, high pressure), GB

petroleum and gas production, NG

natural gas, at production (natural gas, high pressure), NG

petroleum and gas production, NL

natural gas, at production (natural gas, high pressure), NL

petroleum and gas production, NO

natural gas, at production (natural gas, high pressure), NO

The original natural gas datasets are preserved, but they do not provide input to any other datasets in the database. The new datasets provide natural gas at high pressure to the original supply chains, which remain unchanged.

The table below lists the names of the new activities (only high pressure datasets are shown).

Natural gas extraction

location

natural gas, at production

AZ

natural gas, at production

RO

natural gas, at production

LY

natural gas, at production

SA

natural gas, at production

IQ

natural gas, at production

RU

natural gas, at production

NL

natural gas, at production

DZ

natural gas, at production

NG

natural gas, at production

DE

natural gas, at production

KZ

natural gas, at production

NO

natural gas, at production

QA

natural gas, at production

GB

natural gas, at production

MX

natural gas, at production

US

Note

This import does not occur when using ecoinvent v.3.9 as those dataset updates are already included.

Photovoltaic panels

Photovoltaic panel inventories originate the IEA’s Task 12 project IEA_PV. They have been adapted into a brightway2-friendly format. They can be consulted here: LCI_PV.

They consist of the following PV installation types:

PV installation

location

photovoltaic slanted-roof installation, 1.3 MWp, multi-Si, panel, mounted, on roof

CH

photovoltaic flat-roof installation, 156 kWp, multi-Si, on roof

CH

photovoltaic flat-roof installation, 156 kWp, single-Si, on roof

CH

photovoltaic flat-roof installation, 280 kWp, multi-Si, on roof

CH

photovoltaic flat-roof installation, 280 kWp, single-Si, on roof

CH

photovoltaic flat-roof installation, 324 kWp, multi-Si, on roof

DE

photovoltaic slanted-roof installation, 3 kWp, CIS, laminated, integrated, on roof

CH

photovoltaic slanted-roof installation, 3 kWp, CIS, laminated, integrated, on roof

RER

photovoltaic slanted-roof installation, 3 kWp, CdTe, panel, mounted, on roof

CH

photovoltaic slanted-roof installation, 3 kWp, CdTe, panel, mounted, on roof

RER

photovoltaic slanted-roof installation, 3 kWp, micro-Si, laminated, integrated, on roof

RER

photovoltaic slanted-roof installation, 3 kWp, micro-Si, panel, mounted, on roof

RER

photovoltaic flat-roof installation, 450 kWp, single-Si, on roof

DE

photovoltaic open ground installation, 560 kWp, single-Si, on open ground

CH

photovoltaic open ground installation, 569 kWp, multi-Si, on open ground

ES

photovoltaic open ground installation, 570 kWp, CIS, on open ground

RER

photovoltaic open ground installation, 570 kWp, CdTe, on open ground

RER

photovoltaic open ground installation, 570 kWp, micro-Si, on open ground

RER

photovoltaic open ground installation, 570 kWp, multi-Si, on open ground

ES

photovoltaic open ground installation, 570 kWp, multi-Si, on open ground

RER

photovoltaic open ground installation, 570 kWp, single-Si, on open ground

RER

photovoltaic slanted-roof installation, 93 kWp, multi-Si, laminated, integrated, on roof

CH

photovoltaic slanted-roof installation, 93 kWp, multi-Si, panel, mounted, on roof

CH

photovoltaic slanted-roof installation, 93 kWp, single-Si, laminated, integrated, on roof

CH

photovoltaic slanted-roof installation, 93 kWp, single-Si, panel, mounted, on roof

CH

Although these datasets have a limited number of locations (CH, RER, DE, ES), the IEA report provides country-specific load factors:

production [kWh/kWp]

roof-top

façade

central

PT

1427

999

1513

IL

1695

1187

1798

SE

919

643

974

FR

968

678

1026

TR

1388

971

1471

NZ

1240

868

1315

MY

1332

933

1413

CN

971

679

1029

TH

1436

1005

1522

ZA

1634

1144

1733

JP

1024

717

1086

CH

976

683

1040

DE

922

645

978

KR

1129

790

1197

AT

1044

731

1111

GR

1323

926

1402

IE

796

557

844

AU

1240

868

1314

IT

1298

908

1376

MX

1612

1128

1709

NL

937

656

994

GB

848

593

899

ES

1423

996

1509

CL

1603

1122

1699

HU

1090

763

1156

CZ

944

661

1101

CA

1173

821

1243

US

1401

981

1485

NO

832

583

882

FI

891

624

945

BE

908

635

962

DK

971

680

1030

LU

908

635

962

In the report, the generation potential per installation type is multiplied by the number of installations in each country, to produce country-specific PV power mix datasets normalized to 1 kWh. The report specifies the production-weighted PV mix for each country, but we further split it between residential (<=3kWp) and commercial (>3kWp) installations (as most IAMs make such distinction):

Production-weighted PV mix

location

electricity production, photovoltaic, residential

PT

electricity production, photovoltaic, residential

IL

electricity production, photovoltaic, residential

SE

electricity production, photovoltaic, residential

FR

electricity production, photovoltaic, residential

TR

electricity production, photovoltaic, residential

NZ

electricity production, photovoltaic, residential

MY

electricity production, photovoltaic, residential

CN

electricity production, photovoltaic, residential

TH

electricity production, photovoltaic, residential

ZA

electricity production, photovoltaic, residential

JP

electricity production, photovoltaic, residential

CH

electricity production, photovoltaic, residential

DE

electricity production, photovoltaic, residential

KR

electricity production, photovoltaic, residential

AT

electricity production, photovoltaic, residential

GR

electricity production, photovoltaic, residential

IE

electricity production, photovoltaic, residential

AU

electricity production, photovoltaic, residential

IT

electricity production, photovoltaic, residential

MX

electricity production, photovoltaic, residential

NL

electricity production, photovoltaic, residential

GB

electricity production, photovoltaic, residential

ES

electricity production, photovoltaic, residential

CL

electricity production, photovoltaic, residential

HU

electricity production, photovoltaic, residential

CZ

electricity production, photovoltaic, residential

CA

electricity production, photovoltaic, residential

US

electricity production, photovoltaic, residential

NO

electricity production, photovoltaic, residential

FI

electricity production, photovoltaic, residential

BE

electricity production, photovoltaic, residential

DK

electricity production, photovoltaic, residential

LU

electricity production, photovoltaic, commercial

PT

electricity production, photovoltaic, commercial

IL

electricity production, photovoltaic, commercial

SE

electricity production, photovoltaic, commercial

FR

electricity production, photovoltaic, commercial

TR

electricity production, photovoltaic, commercial

NZ

electricity production, photovoltaic, commercial

MY

electricity production, photovoltaic, commercial

CN

electricity production, photovoltaic, commercial

TH

electricity production, photovoltaic, commercial

ZA

electricity production, photovoltaic, commercial

JP

electricity production, photovoltaic, commercial

CH

electricity production, photovoltaic, commercial

DE

electricity production, photovoltaic, commercial

KR

electricity production, photovoltaic, commercial

AT

electricity production, photovoltaic, commercial

GR

electricity production, photovoltaic, commercial

IE

electricity production, photovoltaic, commercial

AU

electricity production, photovoltaic, commercial

IT

electricity production, photovoltaic, commercial

MX

electricity production, photovoltaic, commercial

NL

electricity production, photovoltaic, commercial

GB

electricity production, photovoltaic, commercial

ES

electricity production, photovoltaic, commercial

CL

electricity production, photovoltaic, commercial

HU

electricity production, photovoltaic, commercial

CZ

electricity production, photovoltaic, commercial

CA

electricity production, photovoltaic, commercial

US

electricity production, photovoltaic, commercial

NO

electricity production, photovoltaic, commercial

FI

electricity production, photovoltaic, commercial

BE

electricity production, photovoltaic, commercial

DK

electricity production, photovoltaic, commercial

LU

Hence, inside the residential PV mix of Spain (“electricity production, photovoltaic, residential”), one will find the following inputs for the production of 1kWh:

name

amount

location

unit

Energy, solar, converted

3.8503

megajoule

Heat, waste

0.25027

megajoule

photovoltaic slanted-roof installation, 3 kWp, CIS, laminated, integrated, on roof

2.48441E-08

CH

unit

photovoltaic slanted-roof installation, 3 kWp, CdTe, panel, mounted, on roof

4.99911E-07

CH

unit

photovoltaic slanted-roof installation, 3 kWp, micro-Si, laminated, integrated, on roof

3.93869E-09

RER

unit

photovoltaic slanted-roof installation, 3 kWp, micro-Si, panel, mounted, on roof

6.55186E-08

RER

unit

photovoltaic facade installation, 3kWp, multi-Si, laminated, integrated, at building

2.10481E-07

RER

unit

photovoltaic facade installation, 3kWp, multi-Si, panel, mounted, at building

2.10481E-07

RER

unit

photovoltaic facade installation, 3kWp, single-Si, laminated, integrated, at building

1.11463E-07

RER

unit

photovoltaic facade installation, 3kWp, single-Si, panel, mounted, at building

1.11463E-07

RER

unit

photovoltaic flat-roof installation, 3kWp, multi-Si, on roof

2.20794E-06

RER

unit

photovoltaic flat-roof installation, 3kWp, single-Si, on roof

1.17025E-06

RER

unit

photovoltaic slanted-roof installation, 3kWp, CIS, panel, mounted, on roof

4.12805E-07

CH

unit

photovoltaic slanted-roof installation, 3kWp, CdTe, laminated, integrated, on roof

3.00704E-08

CH

unit

photovoltaic slanted-roof installation, 3kWp, multi-Si, laminated, integrated, on roof

1.08693E-07

RER

unit

photovoltaic slanted-roof installation, 3kWp, multi-Si, panel, mounted, on roof

1.81407E-06

RER

unit

photovoltaic slanted-roof installation, 3kWp, single-Si, laminated, integrated, on roof

5.75655E-08

RER

unit

photovoltaic slanted-roof installation, 3kWp, single-Si, panel, mounted, on roof

9.6195E-07

RER

unit

with, for example, 2.48E-8 units of “photovoltaic slanted-roof installation, 3 kWp, CIS, laminated, integrated, on roof” being calculated as:

1 / (30 [years] * 1423 [kWh/kWp] * 0.32% [share of PV capacity of such type installed in Spain])

Note that commercial PV mix datasets provide electricity at high voltage, unlike residential PV mix datasets, which supply at low voltage only.

Geothermal

Heat production by means of a geothermal well are not represented in ecoinvent. The geothermal power plant construction inventories are from Maeder Bachelor Thesis.

The co-generation unit has been removed and replaced by heat exchanger and district heating pipes. Gross heat output of 1,483 TJ, with 80% efficiency.

The inventories can be consulted here: LCIgeothermal.

They introduce the following datasets (only heat production datasets shown):

Geothermal heat production

location

heat production, deep geothermal

RAS

heat production, deep geothermal

GLO

heat production, deep geothermal

RAF

heat production, deep geothermal

RME

heat production, deep geothermal

RLA

heat production, deep geothermal

RU

heat production, deep geothermal

CA

heat production, deep geothermal

JP

heat production, deep geothermal

US

heat production, deep geothermal

IN

heat production, deep geothermal

CN

heat production, deep geothermal

RER

Hydrogen

premise imports inventories for hydrogen production via the following pathways:

  • Steam Methane Reforming, using natural gas

  • Steam Methane Reforming, using natural gas, with Carbon Capture and Storage

  • Steam Methane Reforming, using bio-methane

  • Steam Methane Reforming, using bio-methane, with Carbon Capture and Storage

  • Auto Thermal Reforming, using natural gas

  • Auto Thermal Reforming, using natural gas, with Carbon Capture and Storage

  • Auto Thermal Reforming, using bio-methane

  • Auto Thermal Reforming, using bio-methane, with Carbon Capture and Storage

  • Woody biomass gasification, using a fluidized bed

  • Woody biomass gasification, using a fluidized bed, with Carbon Capture and Storage

  • Woody biomass gasification, using an entrained flow gasifier

  • Woody biomass gasification, using an entrained flow gasifier, with Carbon Capture and Storage

  • Coal gasification

  • Coal gasification, with Carbon Capture and Storage

  • Electrolysis

  • Thermochemical water splitting

  • Pyrolysis

Inventories using Steam Methane Reforming are from Antonini et al. 2021. They can be consulted here: LCI_SMR. Inventories using Auto Thermal Reforming are from Antonini et al. 2021. They can be consulted here: LCI_ATR. Inventories using Woody biomass gasification are from Antonini2 et al. 2021. They can be consulted here: LCI_woody. Inventories using coal gasification are from Wokaun et al. 2015, but updated with Li et al. 2022, which also provide an option with CCS. They can be consulted here: LCI_coal. Inventories using electrolysis are from Niklas Gerloff. 2021. They can be consulted here: LCI_electrolysis. Inventories for thermochemical water splitting are from Zhang2 et al. 2022. Inventories for pyrolysis are from Al-Qahtani et al. 2021, completed with data from Postels et al., 2016.

The new datasets introduced are listed in the table below (only production datasets are shown).

Hydrogen production

location

hydrogen production, steam methane reforming of natural gas, 25 bar

CH

hydrogen production, steam methane reforming of natural gas, with CCS (MDEA, 98% eff.), 25 bar

CH

hydrogen production, steam methane reforming, from biomethane, high and low temperature, with CCS (MDEA, 98% eff.), 26 bar

CH

hydrogen production, steam methane reforming, from biomethane, high and low temperature, 26 bar

CH

hydrogen production, auto-thermal reforming, from biomethane, 25 bar

CH

hydrogen production, auto-thermal reforming, from biomethane, with CCS (MDEA, 98% eff.), 25 bar

CH

hydrogen production, gaseous, 25 bar, from heatpipe reformer gasification of woody biomass with CCS, at gasification plant

CH

hydrogen production, gaseous, 25 bar, from heatpipe reformer gasification of woody biomass, at gasification plant

CH

hydrogen production, gaseous, 25 bar, from gasification of woody biomass in entrained flow gasifier, with CCS, at gasification plant

CH

hydrogen production, gaseous, 25 bar, from gasification of woody biomass in entrained flow gasifier, at gasification plant

CH

hydrogen production, gaseous, 30 bar, from hard coal gasification and reforming, at coal gasification plant

RER

hydrogen production, gaseous, 30 bar, from PEM electrolysis, from grid electricity

RER

hydrogen production, gaseous, 20 bar, from AEC electrolysis, from grid electricity

RER

hydrogen production, gaseous, 1 bar, from SOEC electrolysis, from grid electricity

RER

hydrogen production, gaseous, 1 bar, from SOEC electrolysis, with steam input, from grid electricity

RER

hydrogen production, gaseous, 25 bar, from thermochemical water splitting, at solar tower

RER

hydrogen production, gaseous, 100 bar, from methane pyrolysis

RER

Hydrogen storage and distribution

A number of datasets relating to hydrogen storage and distribution are also imported.

They are necessary to model the distribution of hydrogen:

  • via re-assigned transmission and distribution CNG pipelines, in a gaseous state

  • via dedicated transmission and distribution hydrogen pipelines, in a gaseous state

  • as a liquid organic compound, by hydrogenation

  • via truck, in a liquid state

  • hydrogen refuelling station

Small and large storage solutions are also provided: * high pressure hydrogen storage tank * geological storage tank

These datasets originate from the work of Wulf et al. 2018, and can be consulted here: LCI_H2_distr. For re-assigned CNG pipelines, which require the hydrogen to be mixed together with oxygen to limit metal embrittlement, some parameters are taken from the work of Cerniauskas et al. 2020.

The datasets introduced are listed in the table below.

Hydrogen distribution

location

hydrogen refuelling station

GLO

high pressure hydrogen storage tank

GLO

pipeline, hydrogen, low pressure distribution network

RER

compressor assembly for transmission hydrogen pipeline

RER

pipeline, hydrogen, high pressure transmission network

RER

zinc coating for hydrogen pipeline

RER

hydrogenation of hydrogen

RER

dehydrogenation of hydrogen

RER

dibenzyltoluene production

RER

solution mining for geological hydrogen storage

RER

geological hydrogen storage

RER

hydrogen embrittlement inhibition

RER

distribution pipeline for hydrogen, reassigned CNG pipeline

RER

transmission pipeline for hydrogen, reassigned CNG pipeline

RER

Hydrogen turbine

A dataset for a hydrogen turbine is also imported, to model the production of electricity from hydrogen, with an efficiency of 51%. The efficiency of the H2-fed gas turbine is based on the parameters of Ozawa et al. (2019), accessible here: LCI_H2_turbine.

Biofuels

Inventories for energy crops- and residues-based production of bioethanol and biodiesel are imported, and can be accessed here: LCI_biofuels. They include the farming of the crop, the conversion of the biomass to fuel, as well as its distribution. The conversion process often leads to the production of co-products (dried distiller’s grain, electricity, CO2, bagasse.). Hence, energy, economic and system expansion partitioning approaches are available. These inventories originate from several different sources (Wu et al. 2006 (2020 update), Cozzolino 2018, Pereira et al. 2019 and Gonzalez-Garcia et al. 2012), Cavalett & Cherubini 2022, as indicated in the table below.

The following datasets are introduced:

Activity

Location

Source

Farming and supply of switchgrass

US

Wu et al. 2006 (2020 update)

Farming and supply of poplar

US

Wu et al. 2006 (2020 update)

Farming and supply of willow

US

Wu et al. 2006 (2020 update)

Supply of forest residue

US

Wu et al. 2006 (2020 update)

Farming and supply of miscanthus

US

Wu et al. 2006 (2020 update)

Farming and supply of corn stover

US

Wu et al. 2006 (2020 update)

Farming and supply of sugarcane

US

Wu et al. 2006 (2020 update)

Farming and supply of Grain Sorghum

US

Wu et al. 2006 (2020 update)

Farming and supply of Sweet Sorghum

US

Wu et al. 2006 (2020 update)

Farming and supply of Forage Sorghum

US

Wu et al. 2006 (2020 update)

Farming and supply of corn

US

Wu et al. 2006 (2020 update)

Farming and supply of sugarcane

BR

Pereira et al. 2019/RED II

Farming and supply of sugarcane straw

BR

Pereira et al. 2019

Farming and supply of eucalyptus

ES

Gonzalez-Garcia et al. 2012

Farming and supply of wheat grains

RER

Cozzolino 2018

Farming and supply of wheat straw

RER

Cozzolino 2018

Farming and supply of corn

RER

Cozzolino 2018/RED II

Farming and supply of sugarbeet

RER

Cozzolino 2018

Supply of forest residue

RER

Cozzolino 2018

Supply and refining of waste cooking oil

RER

Cozzolino 2018

Farming and supply of rapeseed

RER

Cozzolino 2018/RED II

Farming and supply of palm fresh fruit bunch

RER

Cozzolino 2018

Farming and supply of dry algae

RER

Cozzolino 2018

Ethanol production, via fermentation, from switchgrass

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from poplar

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from willow

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from forest residue

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from miscanthus

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from corn stover

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from sugarcane

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from grain sorghum

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from sweet sorghum

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from forage sorghum

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from corn

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from corn, with carbon capture

US

Wu et al. 2006 (2020 update)

Ethanol production, via fermentation, from sugarcane

BR

Pereira et al. 2019

Ethanol production, via fermentation, from sugarcane straw

BR

Pereira et al. 2019

Ethanol production, via fermentation, from eucalyptus

ES

Gonzalez-Garcia et al. 2012

Ethanol production, via fermentation, from wheat grains

RER

Cozzolino 2018

Ethanol production, via fermentation, from wheat straw

RER

Cozzolino 2018

Ethanol production, via fermentation, from corn starch

RER

Cozzolino 2018

Ethanol production, via fermentation, from sugarbeet

RER

Cozzolino 2018

Ethanol production, via fermentation, from forest residue

RER

Cozzolino 2018

Ethanol production, via fermentation, from forest residues

RER

Cavalett & Cherubini 2022

Ethanol production, via fermentation, from forest product (non-residual)

RER

Cavalett & Cherubini 2022

Biodiesel production, via transesterification, from used cooking oil

RER

Cozzolino 2018

Biodiesel production, via transesterification, from rapeseed oil

RER

Cozzolino 2018

Biodiesel production, via transesterification, from palm oil, energy allocation

RER

Cozzolino 2018

Biodiesel production, via transesterification, from algae, energy allocation

RER

Cozzolino 2018

Biodiesel production, via Fischer-Tropsch, from forest residues

RER

Cavalett & Cherubini 2022

Biodiesel production, via Fischer-Tropsch, from forest product (non-residual)

RER

Cavalett & Cherubini 2022

Kerosene production, via Fischer-Tropsch, from forest residues

RER

Cavalett & Cherubini 2022

Kerosene production, via Fischer-Tropsch, from forest product (non-residual)

RER

Cavalett & Cherubini 2022

Synthetic fuels

premise imports inventories for the synthesis of hydrocarbon fuels following two pathways:

  • Fischer-Tropsch: it uses hydrogen and CO (from CO2 via a reverse water gas shift process) to produce “syncrude”, which is distilled into diesel, kerosene, naphtha and lubricating oil and waxes. Inventories are from van der Giesen et al. 2014.

  • Methanol-to-liquids: methanol is synthesized from hydrogen and CO2, and further distilled into gasoline, diesel, LGP and kerosene. Synthetic methanol inventories are from Hank et al. 2019. The methanol to fuel process specifications are from FVV 2013.

  • Electro-chemical methanation: methane is produced from hydrogen and CO2 using a Sabatier methanation reactor. Inventories are from Zhang et al, 2019.

In their default configuration, these fuels use hydrogen from electrolysis and CO2 from direct air capture (DAC). However, premise builds different configurations (i.e., CO2 and hydrogen sources) for these fuels, for each IAM region:

Fuel production dataset

location

source

Diesel production, synthetic, from Fischer Tropsch process, hydrogen from coal gasification, at fuelling station

all IAM regions

van der Giesen et al. 2014

Diesel production, synthetic, from Fischer Tropsch process, hydrogen from coal gasification, with CCS, at fuelling station

all IAM regions

van der Giesen et al. 2014

Diesel production, synthetic, from Fischer Tropsch process, hydrogen from electrolysis, at fuelling station

all IAM regions

van der Giesen et al. 2014

Diesel production, synthetic, from Fischer Tropsch process, hydrogen from wood gasification, at fuelling station

all IAM regions

van der Giesen et al. 2014

Diesel production, synthetic, from Fischer Tropsch process, hydrogen from wood gasification, with CCS, at fuelling station

all IAM regions

van der Giesen et al. 2014

Diesel production, synthetic, from methanol, hydrogen from coal gasification, at fuelling station

all IAM regions

Hank et al, 2019

Diesel production, synthetic, from methanol, hydrogen from coal gasification, with CCS, at fuelling station

all IAM regions

Hank et al, 2019

Diesel production, synthetic, from methanol, hydrogen from electrolysis, CO2 from cement plant, at fuelling station

all IAM regions

Hank et al, 2019

Diesel production, synthetic, from methanol, hydrogen from electrolysis, CO2 from DAC, at fuelling station

all IAM regions

Hank et al, 2019

Gasoline production, synthetic, from methanol, hydrogen from coal gasification, at fuelling station

all IAM regions

Hank et al, 2019

Gasoline production, synthetic, from methanol, hydrogen from coal gasification, with CCS, at fuelling station

all IAM regions

Hank et al, 2019

Gasoline production, synthetic, from methanol, hydrogen from electrolysis, CO2 from cement plant, at fuelling station

all IAM regions

Hank et al, 2019

Gasoline production, synthetic, from methanol, hydrogen from electrolysis, CO2 from DAC, at fuelling station

all IAM regions

Hank et al, 2019

Kerosene production, from methanol, hydrogen from coal gasification

all IAM regions

Hank et al, 2019

Kerosene production, from methanol, hydrogen from electrolysis, CO2 from cement plant

all IAM regions

Hank et al, 2019

Kerosene production, from methanol, hydrogen from electrolysis, CO2 from DAC

all IAM regions

Hank et al, 2019

Kerosene production, synthetic, Fischer Tropsch process, hydrogen from coal gasification

all IAM regions

van der Giesen et al. 2014

Kerosene production, synthetic, Fischer Tropsch process, hydrogen from coal gasification, with CCS

all IAM regions

van der Giesen et al. 2014

Kerosene production, synthetic, Fischer Tropsch process, hydrogen from electrolysis

all IAM regions

van der Giesen et al. 2014

Kerosene production, synthetic, Fischer Tropsch process, hydrogen from wood gasification

all IAM regions

van der Giesen et al. 2014

Kerosene production, synthetic, Fischer Tropsch process, hydrogen from wood gasification, with CCS

all IAM regions

van der Giesen et al. 2014

Lubricating oil production, synthetic, Fischer Tropsch process, hydrogen from coal gasification

all IAM regions

van der Giesen et al. 2014

Lubricating oil production, synthetic, Fischer Tropsch process, hydrogen from electrolysis

all IAM regions

van der Giesen et al. 2014

Lubricating oil production, synthetic, Fischer Tropsch process, hydrogen from wood gasification

all IAM regions

van der Giesen et al. 2014

Lubricating oil production, synthetic, Fischer Tropsch process, hydrogen from wood gasification, with CCS

all IAM regions

van der Giesen et al. 2014

Methane, synthetic, gaseous, 5 bar, from coal-based hydrogen, at fuelling station

all IAM regions

Zhang et al, 2019

Methane, synthetic, gaseous, 5 bar, from electrochemical methanation (H2 from electrolysis, CO2 from DAC using heat pump heat), at fuelling station, using heat pump heat

all IAM regions

Zhang et al, 2019

Methane, synthetic, gaseous, 5 bar, from electrochemical methanation (H2 from electrolysis, CO2 from DAC using waste heat), at fuelling station, using waste heat

all IAM regions

Zhang et al, 2019

Methane, synthetic, gaseous, 5 bar, from electrochemical methanation, at fuelling station

all IAM regions

Zhang et al, 2019

Naphtha production, synthetic, Fischer Tropsch process, hydrogen from coal gasification

all IAM regions

van der Giesen et al. 2014

Naphtha production, synthetic, Fischer Tropsch process, hydrogen from electrolysis

all IAM regions

van der Giesen et al. 2014

Naphtha production, synthetic, Fischer Tropsch process, hydrogen from wood gasification

all IAM regions

van der Giesen et al. 2014

Naphtha production, synthetic, Fischer Tropsch process, hydrogen from wood gasification, with CCS

all IAM regions

van der Giesen et al. 2014

Liquefied petroleum gas production, synthetic, from methanol, hydrogen from electrolysis, CO2 from DAC, at fuelling station

all IAM regions

Hank et al, 2019

In the case of wood and coal gasification-based fuels, the CO2 needed to produce methanol or syncrude originates from the gasification process itself. This also implies that in the methanol and/or RWGS process, a carbon balance correction is applied to reflect the fact that a part of the CO2 from the gasification process is redirected into the fuel production process.

If the CO2 originates from:

  • a gasification process without CCS, a negative carbon correction is added to

reflect the fact that part of the CO2 has not been emitted but has ended in the fuel instead. * the gasification process with CCS, no carbon correction is necessary, because the CO2 is stored in the fuel instead of being stored underground, which from a carbon accounting standpoint is similar.

Carbon Capture

Two sets of inventories for Direct Air Capture (DAC) are available in premise. One for a solvent-based system, and one for a sorbent-based system. The inventories were developed by Qiu and are available in the LCI_DAC spreadsheet. For each, a variant including the subsequent compression, transport and storage of the captured CO2 is also available.

They can be consulted here: LCI_DAC.

Additional, two datasets for carbon capture at point sources are available: one at cement plant from Meunier et al, 2020, and another one at municipal solid waste incineration plant (MSWI) from Bisinella et al, 2021.

They introduce the following datasets:

Activity

Location

carbon dioxide, captured from atmosphere, with a sorbent-based direct air capture system, 100ktCO2

RER

carbon dioxide, captured from atmosphere and stored, with a sorbent-based direct air capture system, 100ktCO2

RER

carbon dioxide, captured from atmosphere, with a solvent-based direct air capture system, 1MtCO2

RER

carbon dioxide, captured from atmosphere and stored, with a solvent-based direct air capture system, 1MtCO2

RER

carbon dioxide, captured at municipal solid waste incineration plant, for subsequent reuse

RER

carbon dioxide, captured at cement production plant, for subsequent reuse

RER

Using the transformation function update(“dac”), premise creates various configurations of these processes, using different sources for heat (industrial steam heat, high-temp heat pump heat and excess heat), which are found under the following names, for each IAM region:

name

location

carbon dioxide, captured from atmosphere, with a solvent-based direct air capture system, 1MtCO2, with industrial steam heat, and grid electricity

all IAM regions

carbon dioxide, captured from atmosphere, with a solvent-based direct air capture system, 1MtCO2, with heat pump heat, and grid electricity

all IAM regions

carbon dioxide, captured from atmosphere, with a sorbent-based direct air capture system, 100ktCO2, with waste heat, and grid electricity

all IAM regions

carbon dioxide, captured from atmosphere, with a sorbent-based direct air capture system, 100ktCO2, with industrial steam heat, and grid electricity

all IAM regions

carbon dioxide, captured from atmosphere, with a sorbent-based direct air capture system, 100ktCO2, with heat pump heat, and grid electricity

all IAM regions

Note that only solid sorbent DAC can use waste heat, as the heat requirement for liquid solvent DAC is too high (~900 C)

Li-ion batteries

When using ecoinvent 3.8 as a database, premise imports new inventories for lithium-ion batteries. NMC-111, NMC-6222 NMC-811 and NCA Lithium-ion battery inventories are originally from Dai et al. 2019. They have been adapted to ecoinvent by Crenna et al, 2021. LFP and LTO Lithium-ion battery inventories are from Schmidt et al. 2019. Li-S battery inventories are from Wickerts et al. 2023. Li-O2 battery inventories are from Wang et al. 2020. Finally, SIB battery inventories are from Zhang22 et al. 2024.

They introduce the following datasets:

Battery components

location

source

battery management system production, for Li-ion battery

GLO

Schmidt et al. 2019

battery cell production, Li-ion, NMC111

GLO

Dai et al. 2019, Crenna et al. 2021

battery cell production, Li-ion, NMC622

GLO

Dai et al. 2019, Crenna et al. 2021

battery cell production, Li-ion, NMC811

GLO

Dai et al. 2019, Crenna et al. 2021

battery cell production, Li-ion, NCA

GLO

Dai et al. 2019, Crenna et al. 2021

battery cell production, Li-ion, LFP

GLO

Schmidt et al. 2019

battery cell production, Li-ion, LTO

GLO

Schmidt et al. 2019

battery cell production, Li-S

GLO

Wickerts et al. (2023)

battery cell production, Li-O2

GLO

Wang et al. (2020)

battery cell production, SIB

GLO

Zhang et al. (2024)

These battery inventories are mostly used by battery electric vehicles, stationary energy storage systems, etc. (also imported by premise).

NMC-111, NMC-811, LFP and NCA inventories can be found here: LCI_batteries1. NMC-622 and LTO inventories can be found here: LCI_batteries2. Li-S inventories can be found here: LCI_batteries3. Li-O2 inventories can be found here: LCI_batteries4. And SIB inventories can be found here: LCI_batteries5.

When using ecoinvent 3.9 and above, the NMC-111, NMC-811, LFP and NCA battery inventories are not imported (as are already present the ecoinvent database).

Graphite

premise includes new inventories for:

  • natural graphite, from Engels et al. 2022,

  • synthetic graphite, from Surovtseva et al. 2022,

forming a new market for graphite, with the following datasets:

Activity

Location

market for graphite, battery grade

1.0

graphite, natural

CN

0.8

graphite, synthetic

CN

0.2

to represent a 80:20 split between natural and synthetic graphite, according to Surovtseva et al, 2022.

These inventories can be found here: LCI_graphite.

Cobalt

New inventories of cobalt are added, from the work of Dai, Kelly and Elgowainy, 2018. They are available under the following datasets:

Activity

Location

cobalt sulfate production, from copper mining, economic allocation

CN

cobalt sulfate production, from copper mining, energy allocation

CN

cobalt metal production, from copper mining, via electrolysis, economic allocation

CN

cobalt metal production, from copper mining, via electrolysis, energy allocation

CN

We recommend using those rather than the original ecoinvent inventories for cobalt, provided by the Cobalt Development Institute (CDI) since ecoinvent 3.7, which seem to lack transparency.

These inventories can be found here: LCI_cobalt.

Lithium

New inventories for lithium extraction are also added, from the work of Schenker et al., 2022. They cover lithium extraction from five different locations in Chile, Argentina and China. They are available under the following datasets for battery production:

Activity

Location

market for lithium carbonate, battery grade

GLO

market for lithium hydroxide, battery grade

GLO

These inventories can be found here: LCI_lithium.

Vanadium Redox Flow Batteries

premise imports inventories for the production of a vanadium redox flow battery, used for grid-balancing, from the work of Weber et al. 2021. It is available under the following dataset:

  • vanadium-redox flow battery system assembly, 8.3 megawatt hour

The dataset providing electricity is the following:

  • electricity supply, high voltage, from vanadium-redox flow battery system

The power capacity for this application is 1MW and the net storage capacity 6 MWh. The net capacity considers the internal inefficiencies of the batteries and the min Sate-of-Charge, requiring a certain oversizing of the batteries. For providing net 6 MWh, a nominal capacity of 8.3 MWh is required for the VRFB with the assumed operation parameters. The assumed lifetime of the stack is 10 years. The lifetime of the system is 20 years or 8176 cycle-life (49,000 MWh).

These inventories can be found here: LCI_vanadium_redox_flow_batteries.

This publication also provides LCIs for Vanadium mining and refining from iron ore. The end product is vanadium pentoxide, which is available under the following dataset:

  • vanadium pentoxide production

These inventories can be found here: LCI_vanadium.

Road vehicles

premise imports inventories for different types of on-road vehicles.

Two-wheelers

The following datasets for two-wheelers are imported. Inventories are from Sacchi et al. 2022. The vehicles are available for different years and emission standards. premise will only import vehicles which production year is equal or inferior to the scenario year considered. The inventories can be consulted here: LCItwowheelers.

Two-wheeler datasets

location

transport, Kick Scooter, electric, <1kW

all IAM regions

transport, Bicycle, conventional, urban

all IAM regions

transport, Bicycle, electric (<25 km/h)

all IAM regions

transport, Bicycle, electric (<45 km/h)

all IAM regions

transport, Bicycle, electric, cargo bike

all IAM regions

transport, Moped, gasoline, <4kW, EURO-3

all IAM regions

transport, Moped, gasoline, <4kW, EURO-4

all IAM regions

transport, Moped, gasoline, <4kW, EURO-5

all IAM regions

transport, Scooter, gasoline, <4kW, EURO-3

all IAM regions

transport, Scooter, gasoline, <4kW, EURO-4

all IAM regions

transport, Scooter, gasoline, <4kW, EURO-5

all IAM regions

transport, Scooter, gasoline, 4-11kW, EURO-3

all IAM regions

transport, Scooter, gasoline, 4-11kW, EURO-4

all IAM regions

transport, Scooter, gasoline, 4-11kW, EURO-5

all IAM regions

transport, Scooter, electric, <4kW

all IAM regions

transport, Scooter, electric, 4-11kW

all IAM regions

transport, Motorbike, gasoline, 4-11kW, EURO-3

all IAM regions

transport, Motorbike, gasoline, 4-11kW, EURO-4

all IAM regions

transport, Motorbike, gasoline, 4-11kW, EURO-5

all IAM regions

transport, Motorbike, gasoline, 11-35kW, EURO-3

all IAM regions

transport, Motorbike, gasoline, 11-35kW, EURO-4

all IAM regions

transport, Motorbike, gasoline, 11-35kW, EURO-5

all IAM regions

transport, Motorbike, gasoline, >35kW, EURO-3

all IAM regions

transport, Motorbike, gasoline, >35kW, EURO-4

all IAM regions

transport, Motorbike, gasoline, >35kW, EURO-5

all IAM regions

transport, Motorbike, electric, <4kW

all IAM regions

transport, Motorbike, electric, 4-11kW

all IAM regions

transport, Motorbike, electric, 11-35kW

all IAM regions

transport, Motorbike, electric, >35kW

all IAM regions

These inventories do not supply inputs to other activities in the LCI database. As such, they are optional.

Passenger cars

The following datasets for passenger cars are imported.

Passenger car datasets

location

transport, passenger car, gasoline, Large, EURO-2

all IAM regions

transport, passenger car, gasoline, Large, EURO-3

all IAM regions

transport, passenger car, gasoline, Large, EURO-4

all IAM regions

transport, passenger car, gasoline, Large, EURO-6ab

all IAM regions

transport, passenger car, gasoline, Large, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline, Large, EURO-6d

all IAM regions

transport, passenger car, diesel, Large, EURO-2

all IAM regions

transport, passenger car, diesel, Large, EURO-3

all IAM regions

transport, passenger car, diesel, Large, EURO-4

all IAM regions

transport, passenger car, diesel, Large, EURO-6ab

all IAM regions

transport, passenger car, diesel, Large, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel, Large, EURO-6d

all IAM regions

transport, passenger car, compressed gas, Large, EURO-2

all IAM regions

transport, passenger car, compressed gas, Large, EURO-3

all IAM regions

transport, passenger car, compressed gas, Large, EURO-4

all IAM regions

transport, passenger car, compressed gas, Large, EURO-6ab

all IAM regions

transport, passenger car, compressed gas, Large, EURO-6d-TEMP

all IAM regions

transport, passenger car, compressed gas, Large, EURO-6d

all IAM regions

transport, passenger car, plugin gasoline hybrid, Large, EURO-6ab

all IAM regions

transport, passenger car, plugin gasoline hybrid, Large, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin gasoline hybrid, Large, EURO-6d

all IAM regions

transport, passenger car, plugin diesel hybrid, Large, EURO-6ab

all IAM regions

transport, passenger car, plugin diesel hybrid, Large, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin diesel hybrid, Large, EURO-6d

all IAM regions

transport, passenger car, fuel cell electric, Large

all IAM regions

transport, passenger car, battery electric, NMC-622 battery, Large

all IAM regions

transport, passenger car, gasoline hybrid, Large, EURO-6ab

all IAM regions

transport, passenger car, gasoline hybrid, Large, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline hybrid, Large, EURO-6d

all IAM regions

transport, passenger car, diesel hybrid, Large, EURO-6ab

all IAM regions

transport, passenger car, diesel hybrid, Large, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel hybrid, Large, EURO-6d

all IAM regions

transport, passenger car, gasoline, Large SUV, EURO-2

all IAM regions

transport, passenger car, gasoline, Large SUV, EURO-3

all IAM regions

transport, passenger car, gasoline, Large SUV, EURO-4

all IAM regions

transport, passenger car, gasoline, Large SUV, EURO-6ab

all IAM regions

transport, passenger car, gasoline, Large SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline, Large SUV, EURO-6d

all IAM regions

transport, passenger car, diesel, Large SUV, EURO-2

all IAM regions

transport, passenger car, diesel, Large SUV, EURO-3

all IAM regions

transport, passenger car, diesel, Large SUV, EURO-4

all IAM regions

transport, passenger car, diesel, Large SUV, EURO-6ab

all IAM regions

transport, passenger car, diesel, Large SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel, Large SUV, EURO-6d

all IAM regions

transport, passenger car, compressed gas, Large SUV, EURO-2

all IAM regions

transport, passenger car, compressed gas, Large SUV, EURO-3

all IAM regions

transport, passenger car, compressed gas, Large SUV, EURO-4

all IAM regions

transport, passenger car, compressed gas, Large SUV, EURO-6ab

all IAM regions

transport, passenger car, compressed gas, Large SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, compressed gas, Large SUV, EURO-6d

all IAM regions

transport, passenger car, plugin gasoline hybrid, Large SUV, EURO-6ab

all IAM regions

transport, passenger car, plugin gasoline hybrid, Large SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin gasoline hybrid, Large SUV, EURO-6d

all IAM regions

transport, passenger car, plugin diesel hybrid, Large SUV, EURO-6ab

all IAM regions

transport, passenger car, plugin diesel hybrid, Large SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin diesel hybrid, Large SUV, EURO-6d

all IAM regions

transport, passenger car, fuel cell electric, Large SUV

all IAM regions

transport, passenger car, battery electric, NMC-622 battery, Large SUV

all IAM regions

transport, passenger car, gasoline hybrid, Large SUV, EURO-6ab

all IAM regions

transport, passenger car, gasoline hybrid, Large SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline hybrid, Large SUV, EURO-6d

all IAM regions

transport, passenger car, diesel hybrid, Large SUV, EURO-6ab

all IAM regions

transport, passenger car, diesel hybrid, Large SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel hybrid, Large SUV, EURO-6d

all IAM regions

transport, passenger car, gasoline, Lower medium, EURO-2

all IAM regions

transport, passenger car, gasoline, Lower medium, EURO-3

all IAM regions

transport, passenger car, gasoline, Lower medium, EURO-4

all IAM regions

transport, passenger car, gasoline, Lower medium, EURO-6ab

all IAM regions

transport, passenger car, gasoline, Lower medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline, Lower medium, EURO-6d

all IAM regions

transport, passenger car, diesel, Lower medium, EURO-2

all IAM regions

transport, passenger car, diesel, Lower medium, EURO-3

all IAM regions

transport, passenger car, diesel, Lower medium, EURO-4

all IAM regions

transport, passenger car, diesel, Lower medium, EURO-6ab

all IAM regions

transport, passenger car, diesel, Lower medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel, Lower medium, EURO-6d

all IAM regions

transport, passenger car, compressed gas, Lower medium, EURO-2

all IAM regions

transport, passenger car, compressed gas, Lower medium, EURO-3

all IAM regions

transport, passenger car, compressed gas, Lower medium, EURO-4

all IAM regions

transport, passenger car, compressed gas, Lower medium, EURO-6ab

all IAM regions

transport, passenger car, compressed gas, Lower medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, compressed gas, Lower medium, EURO-6d

all IAM regions

transport, passenger car, plugin gasoline hybrid, Lower medium, EURO-6ab

all IAM regions

transport, passenger car, plugin gasoline hybrid, Lower medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin gasoline hybrid, Lower medium, EURO-6d

all IAM regions

transport, passenger car, plugin diesel hybrid, Lower medium, EURO-6ab

all IAM regions

transport, passenger car, plugin diesel hybrid, Lower medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin diesel hybrid, Lower medium, EURO-6d

all IAM regions

transport, passenger car, fuel cell electric, Lower medium

all IAM regions

transport, passenger car, battery electric, NMC-622 battery, Lower medium

all IAM regions

transport, passenger car, gasoline hybrid, Lower medium, EURO-6ab

all IAM regions

transport, passenger car, gasoline hybrid, Lower medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline hybrid, Lower medium, EURO-6d

all IAM regions

transport, passenger car, diesel hybrid, Lower medium, EURO-6ab

all IAM regions

transport, passenger car, diesel hybrid, Lower medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel hybrid, Lower medium, EURO-6d

all IAM regions

transport, passenger car, gasoline, Medium, EURO-2

all IAM regions

transport, passenger car, gasoline, Medium, EURO-3

all IAM regions

transport, passenger car, gasoline, Medium, EURO-4

all IAM regions

transport, passenger car, gasoline, Medium, EURO-6ab

all IAM regions

transport, passenger car, gasoline, Medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline, Medium, EURO-6d

all IAM regions

transport, passenger car, diesel, Medium, EURO-2

all IAM regions

transport, passenger car, diesel, Medium, EURO-3

all IAM regions

transport, passenger car, diesel, Medium, EURO-4

all IAM regions

transport, passenger car, diesel, Medium, EURO-6ab

all IAM regions

transport, passenger car, diesel, Medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel, Medium, EURO-6d

all IAM regions

transport, passenger car, compressed gas, Medium, EURO-2

all IAM regions

transport, passenger car, compressed gas, Medium, EURO-3

all IAM regions

transport, passenger car, compressed gas, Medium, EURO-4

all IAM regions

transport, passenger car, compressed gas, Medium, EURO-6ab

all IAM regions

transport, passenger car, compressed gas, Medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, compressed gas, Medium, EURO-6d

all IAM regions

transport, passenger car, plugin gasoline hybrid, Medium, EURO-6ab

all IAM regions

transport, passenger car, plugin gasoline hybrid, Medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin gasoline hybrid, Medium, EURO-6d

all IAM regions

transport, passenger car, plugin diesel hybrid, Medium, EURO-6ab

all IAM regions

transport, passenger car, plugin diesel hybrid, Medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin diesel hybrid, Medium, EURO-6d

all IAM regions

transport, passenger car, fuel cell electric, Medium

all IAM regions

transport, passenger car, battery electric, NMC-622 battery, Medium

all IAM regions

transport, passenger car, gasoline hybrid, Medium, EURO-6ab

all IAM regions

transport, passenger car, gasoline hybrid, Medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline hybrid, Medium, EURO-6d

all IAM regions

transport, passenger car, diesel hybrid, Medium, EURO-6ab

all IAM regions

transport, passenger car, diesel hybrid, Medium, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel hybrid, Medium, EURO-6d

all IAM regions

transport, passenger car, gasoline, Medium SUV, EURO-2

all IAM regions

transport, passenger car, gasoline, Medium SUV, EURO-3

all IAM regions

transport, passenger car, gasoline, Medium SUV, EURO-4

all IAM regions

transport, passenger car, gasoline, Medium SUV, EURO-6ab

all IAM regions

transport, passenger car, gasoline, Medium SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline, Medium SUV, EURO-6d

all IAM regions

transport, passenger car, diesel, Medium SUV, EURO-2

all IAM regions

transport, passenger car, diesel, Medium SUV, EURO-3

all IAM regions

transport, passenger car, diesel, Medium SUV, EURO-4

all IAM regions

transport, passenger car, diesel, Medium SUV, EURO-6ab

all IAM regions

transport, passenger car, diesel, Medium SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel, Medium SUV, EURO-6d

all IAM regions

transport, passenger car, compressed gas, Medium SUV, EURO-2

all IAM regions

transport, passenger car, compressed gas, Medium SUV, EURO-3

all IAM regions

transport, passenger car, compressed gas, Medium SUV, EURO-4

all IAM regions

transport, passenger car, compressed gas, Medium SUV, EURO-6ab

all IAM regions

transport, passenger car, compressed gas, Medium SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, compressed gas, Medium SUV, EURO-6d

all IAM regions

transport, passenger car, plugin gasoline hybrid, Medium SUV, EURO-6ab

all IAM regions

transport, passenger car, plugin gasoline hybrid, Medium SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin gasoline hybrid, Medium SUV, EURO-6d

all IAM regions

transport, passenger car, plugin diesel hybrid, Medium SUV, EURO-6ab

all IAM regions

transport, passenger car, plugin diesel hybrid, Medium SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin diesel hybrid, Medium SUV, EURO-6d

all IAM regions

transport, passenger car, fuel cell electric, Medium SUV

all IAM regions

transport, passenger car, battery electric, NMC-622 battery, Medium SUV

all IAM regions

transport, passenger car, gasoline hybrid, Medium SUV, EURO-6ab

all IAM regions

transport, passenger car, gasoline hybrid, Medium SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline hybrid, Medium SUV, EURO-6d

all IAM regions

transport, passenger car, diesel hybrid, Medium SUV, EURO-6ab

all IAM regions

transport, passenger car, diesel hybrid, Medium SUV, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel hybrid, Medium SUV, EURO-6d

all IAM regions

transport, passenger car, battery electric, NMC-622 battery, Micro

all IAM regions

transport, passenger car, gasoline, Mini, EURO-2

all IAM regions

transport, passenger car, gasoline, Mini, EURO-3

all IAM regions

transport, passenger car, gasoline, Mini, EURO-4

all IAM regions

transport, passenger car, gasoline, Mini, EURO-6ab

all IAM regions

transport, passenger car, gasoline, Mini, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline, Mini, EURO-6d

all IAM regions

transport, passenger car, diesel, Mini, EURO-2

all IAM regions

transport, passenger car, diesel, Mini, EURO-3

all IAM regions

transport, passenger car, diesel, Mini, EURO-4

all IAM regions

transport, passenger car, diesel, Mini, EURO-6ab

all IAM regions

transport, passenger car, diesel, Mini, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel, Mini, EURO-6d

all IAM regions

transport, passenger car, compressed gas, Mini, EURO-2

all IAM regions

transport, passenger car, compressed gas, Mini, EURO-3

all IAM regions

transport, passenger car, compressed gas, Mini, EURO-4

all IAM regions

transport, passenger car, compressed gas, Mini, EURO-6ab

all IAM regions

transport, passenger car, compressed gas, Mini, EURO-6d-TEMP

all IAM regions

transport, passenger car, compressed gas, Mini, EURO-6d

all IAM regions

transport, passenger car, plugin gasoline hybrid, Mini, EURO-6ab

all IAM regions

transport, passenger car, plugin gasoline hybrid, Mini, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin gasoline hybrid, Mini, EURO-6d

all IAM regions

transport, passenger car, plugin diesel hybrid, Mini, EURO-6ab

all IAM regions

transport, passenger car, plugin diesel hybrid, Mini, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin diesel hybrid, Mini, EURO-6d

all IAM regions

transport, passenger car, fuel cell electric, Mini

all IAM regions

transport, passenger car, battery electric, NMC-622 battery, Mini

all IAM regions

transport, passenger car, gasoline hybrid, Mini, EURO-6ab

all IAM regions

transport, passenger car, gasoline hybrid, Mini, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline hybrid, Mini, EURO-6d

all IAM regions

transport, passenger car, diesel hybrid, Mini, EURO-6ab

all IAM regions

transport, passenger car, diesel hybrid, Mini, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel hybrid, Mini, EURO-6d

all IAM regions

transport, passenger car, gasoline, Small, EURO-2

all IAM regions

transport, passenger car, gasoline, Small, EURO-3

all IAM regions

transport, passenger car, gasoline, Small, EURO-4

all IAM regions

transport, passenger car, gasoline, Small, EURO-6ab

all IAM regions

transport, passenger car, gasoline, Small, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline, Small, EURO-6d

all IAM regions

transport, passenger car, diesel, Small, EURO-2

all IAM regions

transport, passenger car, diesel, Small, EURO-3

all IAM regions

transport, passenger car, diesel, Small, EURO-4

all IAM regions

transport, passenger car, diesel, Small, EURO-6ab

all IAM regions

transport, passenger car, diesel, Small, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel, Small, EURO-6d

all IAM regions

transport, passenger car, compressed gas, Small, EURO-2

all IAM regions

transport, passenger car, compressed gas, Small, EURO-3

all IAM regions

transport, passenger car, compressed gas, Small, EURO-4

all IAM regions

transport, passenger car, compressed gas, Small, EURO-6ab

all IAM regions

transport, passenger car, compressed gas, Small, EURO-6d-TEMP

all IAM regions

transport, passenger car, compressed gas, Small, EURO-6d

all IAM regions

transport, passenger car, plugin gasoline hybrid, Small, EURO-6ab

all IAM regions

transport, passenger car, plugin gasoline hybrid, Small, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin gasoline hybrid, Small, EURO-6d

all IAM regions

transport, passenger car, plugin diesel hybrid, Small, EURO-6ab

all IAM regions

transport, passenger car, plugin diesel hybrid, Small, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin diesel hybrid, Small, EURO-6d

all IAM regions

transport, passenger car, fuel cell electric, Small

all IAM regions

transport, passenger car, battery electric, NMC-622 battery, Small

all IAM regions

transport, passenger car, gasoline hybrid, Small, EURO-6ab

all IAM regions

transport, passenger car, gasoline hybrid, Small, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline hybrid, Small, EURO-6d

all IAM regions

transport, passenger car, diesel hybrid, Small, EURO-6ab

all IAM regions

transport, passenger car, diesel hybrid, Small, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel hybrid, Small, EURO-6d

all IAM regions

transport, passenger car, gasoline, Van, EURO-2

all IAM regions

transport, passenger car, gasoline, Van, EURO-3

all IAM regions

transport, passenger car, gasoline, Van, EURO-4

all IAM regions

transport, passenger car, gasoline, Van, EURO-6ab

all IAM regions

transport, passenger car, gasoline, Van, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline, Van, EURO-6d

all IAM regions

transport, passenger car, diesel, Van, EURO-2

all IAM regions

transport, passenger car, diesel, Van, EURO-3

all IAM regions

transport, passenger car, diesel, Van, EURO-4

all IAM regions

transport, passenger car, diesel, Van, EURO-6ab

all IAM regions

transport, passenger car, diesel, Van, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel, Van, EURO-6d

all IAM regions

transport, passenger car, compressed gas, Van, EURO-2

all IAM regions

transport, passenger car, compressed gas, Van, EURO-3

all IAM regions

transport, passenger car, compressed gas, Van, EURO-4

all IAM regions

transport, passenger car, compressed gas, Van, EURO-6ab

all IAM regions

transport, passenger car, compressed gas, Van, EURO-6d-TEMP

all IAM regions

transport, passenger car, compressed gas, Van, EURO-6d

all IAM regions

transport, passenger car, plugin gasoline hybrid, Van, EURO-6ab

all IAM regions

transport, passenger car, plugin gasoline hybrid, Van, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin gasoline hybrid, Van, EURO-6d

all IAM regions

transport, passenger car, plugin diesel hybrid, Van, EURO-6ab

all IAM regions

transport, passenger car, plugin diesel hybrid, Van, EURO-6d-TEMP

all IAM regions

transport, passenger car, plugin diesel hybrid, Van, EURO-6d

all IAM regions

transport, passenger car, fuel cell electric, Van

all IAM regions

transport, passenger car, battery electric, NMC-622 battery, Van

all IAM regions

transport, passenger car, gasoline hybrid, Van, EURO-6ab

all IAM regions

transport, passenger car, gasoline hybrid, Van, EURO-6d-TEMP

all IAM regions

transport, passenger car, gasoline hybrid, Van, EURO-6d

all IAM regions

transport, passenger car, diesel hybrid, Van, EURO-6ab

all IAM regions

transport, passenger car, diesel hybrid, Van, EURO-6d-TEMP

all IAM regions

transport, passenger car, diesel hybrid, Van, EURO-6d

all IAM regions

Inventories are from Sacchi2 et al. 2022. The vehicles are available for different years and emission standards and for each IAM region. premise will only import vehicles which production year is equal or inferior to the scenario year considered. premise will create fleet average vehicles during the Transport transformation for each IAM region. The inventories can be consulted here: LCIpasscars.

At the moment. these inventories do not supply inputs to other activities in the LCI database. As such, they are optional.

Medium and heavy duty trucks

The following datasets for medium and heavy-duty trucks are imported.

Truck datasets

location

transport, freight, lorry, battery electric, NMC-622 battery, 3.5t gross weight

all IAM regions

transport, freight, lorry, fuel cell electric, 3.5t gross weight

all IAM regions

transport, freight, lorry, diesel hybrid, 3.5t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, diesel, 3.5t gross weight, EURO-III

all IAM regions

transport, freight, lorry, diesel, 3.5t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, diesel, 3.5t gross weight, EURO-V

all IAM regions

transport, freight, lorry, diesel, 3.5t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, compressed gas, 3.5t gross weight, EURO-III

all IAM regions

transport, freight, lorry, compressed gas, 3.5t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, compressed gas, 3.5t gross weight, EURO-V

all IAM regions

transport, freight, lorry, compressed gas, 3.5t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, plugin diesel hybrid, 3.5t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, battery electric, NMC-622 battery, 7.5t gross weight

all IAM regions

transport, freight, lorry, fuel cell electric, 7.5t gross weight

all IAM regions

transport, freight, lorry, diesel hybrid, 7.5t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, diesel, 7.5t gross weight, EURO-III

all IAM regions

transport, freight, lorry, diesel, 7.5t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, diesel, 7.5t gross weight, EURO-V

all IAM regions

transport, freight, lorry, diesel, 7.5t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, compressed gas, 7.5t gross weight, EURO-III

all IAM regions

transport, freight, lorry, compressed gas, 7.5t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, compressed gas, 7.5t gross weight, EURO-V

all IAM regions

transport, freight, lorry, compressed gas, 7.5t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, plugin diesel hybrid, 7.5t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, battery electric, NMC-622 battery, 18t gross weight

all IAM regions

transport, freight, lorry, fuel cell electric, 18t gross weight

all IAM regions

transport, freight, lorry, diesel hybrid, 18t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, diesel, 18t gross weight, EURO-III

all IAM regions

transport, freight, lorry, diesel, 18t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, diesel, 18t gross weight, EURO-V

all IAM regions

transport, freight, lorry, diesel, 18t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, compressed gas, 18t gross weight, EURO-III

all IAM regions

transport, freight, lorry, compressed gas, 18t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, compressed gas, 18t gross weight, EURO-V

all IAM regions

transport, freight, lorry, compressed gas, 18t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, plugin diesel hybrid, 18t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, battery electric, NMC-622 battery, 26t gross weight

all IAM regions

transport, freight, lorry, fuel cell electric, 26t gross weight

all IAM regions

transport, freight, lorry, diesel hybrid, 26t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, diesel, 26t gross weight, EURO-III

all IAM regions

transport, freight, lorry, diesel, 26t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, diesel, 26t gross weight, EURO-V

all IAM regions

transport, freight, lorry, diesel, 26t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, compressed gas, 26t gross weight, EURO-III

all IAM regions

transport, freight, lorry, compressed gas, 26t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, compressed gas, 26t gross weight, EURO-V

all IAM regions

transport, freight, lorry, compressed gas, 26t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, plugin diesel hybrid, 26t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, battery electric, NMC-622 battery, 32t gross weight

all IAM regions

transport, freight, lorry, fuel cell electric, 32t gross weight

all IAM regions

transport, freight, lorry, diesel hybrid, 32t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, diesel, 32t gross weight, EURO-III

all IAM regions

transport, freight, lorry, diesel, 32t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, diesel, 32t gross weight, EURO-V

all IAM regions

transport, freight, lorry, diesel, 32t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, compressed gas, 32t gross weight, EURO-III

all IAM regions

transport, freight, lorry, compressed gas, 32t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, compressed gas, 32t gross weight, EURO-V

all IAM regions

transport, freight, lorry, compressed gas, 32t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, plugin diesel hybrid, 32t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, battery electric, NMC-622 battery, 40t gross weight

all IAM regions

transport, freight, lorry, fuel cell electric, 40t gross weight

all IAM regions

transport, freight, lorry, diesel hybrid, 40t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, diesel, 40t gross weight, EURO-III

all IAM regions

transport, freight, lorry, diesel, 40t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, diesel, 40t gross weight, EURO-V

all IAM regions

transport, freight, lorry, diesel, 40t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, compressed gas, 40t gross weight, EURO-III

all IAM regions

transport, freight, lorry, compressed gas, 40t gross weight, EURO-IV

all IAM regions

transport, freight, lorry, compressed gas, 40t gross weight, EURO-V

all IAM regions

transport, freight, lorry, compressed gas, 40t gross weight, EURO-VI

all IAM regions

transport, freight, lorry, plugin diesel hybrid, 40t gross weight, EURO-VI

all IAM regions

Inventories are from Sacchi3 et al. 2021. The vehicles are available for different years and emission standards and for each IAM region. premise will only import vehicles which production year is equal or inferior to the scenario year considered. premise will create fleet average vehicles during the Transport transformation for each IAM region. The inventories can be consulted here: LCItrucks.

Buses

The following datasets for city and coach buses are imported.

transport, passenger bus, battery electric - overnight charging, NMC-622 battery, 9m midibus

all IAM regions

transport, passenger bus, battery electric - opportunity charging, LTO battery, 9m midibus

all IAM regions

transport, passenger bus, fuel cell electric, 9m midibus

all IAM regions

transport, passenger bus, diesel hybrid, 9m midibus, EURO-VI

all IAM regions

transport, passenger bus, diesel, 9m midibus, EURO-III

all IAM regions

transport, passenger bus, diesel, 9m midibus, EURO-IV

all IAM regions

transport, passenger bus, diesel, 9m midibus, EURO-V

all IAM regions

transport, passenger bus, diesel, 9m midibus, EURO-VI

all IAM regions

transport, passenger bus, compressed gas, 9m midibus, EURO-III

all IAM regions

transport, passenger bus, compressed gas, 9m midibus, EURO-IV

all IAM regions

transport, passenger bus, compressed gas, 9m midibus, EURO-V

all IAM regions

transport, passenger bus, compressed gas, 9m midibus, EURO-VI

all IAM regions

transport, passenger bus, battery electric - overnight charging, NMC-622 battery, 13m single deck urban bus

all IAM regions

transport, passenger bus, battery electric - battery-equipped trolleybus, LTO battery, 13m single deck urban bus

all IAM regions

transport, passenger bus, battery electric - opportunity charging, LTO battery, 13m single deck urban bus

all IAM regions

transport, passenger bus, fuel cell electric, 13m single deck urban bus

all IAM regions

transport, passenger bus, diesel hybrid, 13m single deck urban bus, EURO-VI

all IAM regions

transport, passenger bus, diesel, 13m single deck urban bus, EURO-III

all IAM regions

transport, passenger bus, diesel, 13m single deck urban bus, EURO-IV

all IAM regions

transport, passenger bus, diesel, 13m single deck urban bus, EURO-V

all IAM regions

transport, passenger bus, diesel, 13m single deck urban bus, EURO-VI

all IAM regions

transport, passenger bus, compressed gas, 13m single deck urban bus, EURO-III

all IAM regions

transport, passenger bus, compressed gas, 13m single deck urban bus, EURO-IV

all IAM regions

transport, passenger bus, compressed gas, 13m single deck urban bus, EURO-V

all IAM regions

transport, passenger bus, compressed gas, 13m single deck urban bus, EURO-VI

all IAM regions

transport, passenger bus, fuel cell electric, 13m single deck coach bus

all IAM regions

transport, passenger bus, diesel hybrid, 13m single deck coach bus, EURO-VI

all IAM regions

transport, passenger bus, diesel, 13m single deck coach bus, EURO-III

all IAM regions

transport, passenger bus, diesel, 13m single deck coach bus, EURO-IV

all IAM regions

transport, passenger bus, diesel, 13m single deck coach bus, EURO-V

all IAM regions

transport, passenger bus, diesel, 13m single deck coach bus, EURO-VI

all IAM regions

transport, passenger bus, compressed gas, 13m single deck coach bus, EURO-III

all IAM regions

transport, passenger bus, compressed gas, 13m single deck coach bus, EURO-IV

all IAM regions

transport, passenger bus, compressed gas, 13m single deck coach bus, EURO-V

all IAM regions

transport, passenger bus, compressed gas, 13m single deck coach bus, EURO-VI

all IAM regions

transport, passenger bus, battery electric - overnight charging, NMC-622 battery, 13m double deck urban bus

all IAM regions

transport, passenger bus, battery electric - opportunity charging, LTO battery, 13m double deck urban bus

all IAM regions

transport, passenger bus, fuel cell electric, 13m double deck urban bus

all IAM regions

transport, passenger bus, diesel hybrid, 13m double deck urban bus, EURO-VI

all IAM regions

transport, passenger bus, diesel, 13m double deck urban bus, EURO-III

all IAM regions

transport, passenger bus, diesel, 13m double deck urban bus, EURO-IV

all IAM regions

transport, passenger bus, diesel, 13m double deck urban bus, EURO-V

all IAM regions

transport, passenger bus, diesel, 13m double deck urban bus, EURO-VI

all IAM regions

transport, passenger bus, compressed gas, 13m double deck urban bus, EURO-III

all IAM regions

transport, passenger bus, compressed gas, 13m double deck urban bus, EURO-IV

all IAM regions

transport, passenger bus, compressed gas, 13m double deck urban bus, EURO-V

all IAM regions

transport, passenger bus, compressed gas, 13m double deck urban bus, EURO-VI

all IAM regions

transport, passenger bus, fuel cell electric, 13m double deck coach bus

all IAM regions

transport, passenger bus, diesel hybrid, 13m double deck coach bus, EURO-VI

all IAM regions

transport, passenger bus, diesel, 13m double deck coach bus, EURO-III

all IAM regions

transport, passenger bus, diesel, 13m double deck coach bus, EURO-IV

all IAM regions

transport, passenger bus, diesel, 13m double deck coach bus, EURO-V

all IAM regions

transport, passenger bus, diesel, 13m double deck coach bus, EURO-VI

all IAM regions

transport, passenger bus, compressed gas, 13m double deck coach bus, EURO-III

all IAM regions

transport, passenger bus, compressed gas, 13m double deck coach bus, EURO-IV

all IAM regions

transport, passenger bus, compressed gas, 13m double deck coach bus, EURO-V

all IAM regions

transport, passenger bus, compressed gas, 13m double deck coach bus, EURO-VI

all IAM regions

transport, passenger bus, battery electric - overnight charging, NMC-622 battery, 18m articulated urban bus

all IAM regions

transport, passenger bus, battery electric - battery-equipped trolleybus, LTO battery, 18m articulated urban bus

all IAM regions

transport, passenger bus, battery electric - opportunity charging, LTO battery, 18m articulated urban bus

all IAM regions

transport, passenger bus, fuel cell electric, 18m articulated urban bus

all IAM regions

transport, passenger bus, diesel hybrid, 18m articulated urban bus, EURO-VI

all IAM regions

transport, passenger bus, diesel, 18m articulated urban bus, EURO-III

all IAM regions

transport, passenger bus, diesel, 18m articulated urban bus, EURO-IV

all IAM regions

transport, passenger bus, diesel, 18m articulated urban bus, EURO-V

all IAM regions

transport, passenger bus, diesel, 18m articulated urban bus, EURO-VI

all IAM regions

transport, passenger bus, compressed gas, 18m articulated urban bus, EURO-III

all IAM regions

transport, passenger bus, compressed gas, 18m articulated urban bus, EURO-IV

all IAM regions

transport, passenger bus, compressed gas, 18m articulated urban bus, EURO-V

all IAM regions

transport, passenger bus, compressed gas, 18m articulated urban bus, EURO-VI

all IAM regions

Inventories are from Sacchi et al. 2021. The vehicles are available for different years and emission standards and for each IAM region. premise will only import vehicles which production year is equal or inferior to the scenario year considered. premise will create fleet average vehicles during the Transport transformation for each IAM region. The inventories can be consulted here: LCIbuses.

At the moment. these inventories do not supply inputs to other activities in the LCI database. As such, they are optional.

Migration between ecoinvent versions

Because the additional inventories that are imported may be composed of exchanges meant to link with an ecoinvent version different than what the user specifies to premise upon the database creation, it is necessary to be able to “translate” the imported inventories so that they correctly link to any ecoinvent version premise is compatible with.

Therefore, premise has a migration map that is used to convert certain exchanges to be compatible with a given ecoinvent version.

This migration map is provided here: migrationmap.

IAM data collection

After extracting the ecoinvent database and additional inventories, premise instantiates the class IAMDataCollection, which collects all sorts of data from the IAM output file and store it into multi-dimensional arrays.

Production volumes

Production volumes for different commodities are collected, for the year and scenario specified by the user. Production volumes are used to build regional markets. For example, for the global market, the volume-based shares of each region are used to reflect their respective supply importance. Another example is for building electricity markets: the respective production volumes of each electricity-producing technology is used to determine the gross supply mix of the market.

The table below shows a non-exhaustive list of correspondences between premise, REMIND, IMAGE and LCI terminology, regarding electricity producing technologies. premise production volumes given for secondary energy carriers for electricity. The mapping file is available in the library root folder: mappingElec_.

name in premise

name in REMIND

name in IMAGE

name in LCI database (only first of several shown)

Biomass CHP

SE|Electricity|Biomass|CHP|w/o CCS

Secondary Energy|Electricity|Biomass|w/o CCS|3

heat and power co-generation, wood chips

Biomass CHP CCS

Secondary Energy|Electricity|Biomass|w/ CCS|2

electricity production, at co-generation power plant/wood, post, pipeline 200km, storage 1000m

Biomass ST

Secondary Energy|Electricity|Biomass|w/o CCS|1

electricity production, at wood burning power plant 20 MW, truck 25km, no CCS

Biomass IGCC CCS

SE|Electricity|Biomass|IGCCC|w/ CCS

Secondary Energy|Electricity|Biomass|w/ CCS|1

electricity production, from CC plant, 100% SNG, truck 25km, post, pipeline 200km, storage 1000m

Biomass IGCC

SE|Electricity|Biomass|IGCC|w/o CCS

Secondary Energy|Electricity|Biomass|w/o CCS|2

electricity production, at BIGCC power plant 450MW, no CCS

Coal PC

SE|Electricity|Coal|PC|w/o CCS

Secondary Energy|Electricity|Coal|w/o CCS|1

electricity production, hard coal

Coal IGCC

SE|Electricity|Coal|IGCC|w/o CCS

Secondary Energy|Electricity|Coal|w/o CCS|2

electricity production, at power plant/hard coal, IGCC, no CCS

Coal PC CCS

SE|Electricity|Coal|PCC|w/ CCS

electricity production, at power plant/hard coal, post, pipeline 200km, storage 1000m

Coal IGCC CCS

SE|Electricity|Coal|IGCCC|w/ CCS

Secondary Energy|Electricity|Coal|w/ CCS|1

electricity production, at power plant/hard coal, pre, pipeline 200km, storage 1000m

Coal CHP

SE|Electricity|Coal|CHP|w/o CCS

Secondary Energy|Electricity|Coal|w/o CCS|3

heat and power co-generation, hard coal

Coal CHP CCS

Secondary Energy|Electricity|Coal|w/ CCS|2

electricity production, at co-generation power plant/hard coal, oxy, pipeline

Gas OC

SE|Electricity|Gas|GT

Secondary Energy|Electricity|Gas|w/o CCS|1

electricity production, natural gas, conventional power plant

Gas CC

SE|Electricity|Gas|CC|w/o CCS

Secondary Energy|Electricity|Gas|w/o CCS|2

electricity production, natural gas, combined cycle power plant

Gas CHP

SE|Electricity|Gas|CHP|w/o CCS

Secondary Energy|Electricity|Gas|w/o CCS|3

heat and power co-generation, natural gas, combined cycle power plant, 400MW electrical

Gas CHP CCS

Secondary Energy|Electricity|Gas|w/ CCS|2

electricity production, at co-generation power plant/natural gas, post, pipeline

Gas CC CCS

SE|Electricity|Gas|w/ CCS

Secondary Energy|Electricity|Gas|w/ CCS|1

electricity production, at power plant/natural gas, pre, pipeline

Geothermal

SE|Electricity|Geothermal

Secondary Energy|Electricity|Other

electricity production, deep geothermal

Hydro

SE|Electricity|Hydro

Secondary Energy|Electricity|Hydro

electricity production, hydro, reservoir

Nuclear

SE|Electricity|Nuclear

Secondary Energy|Electricity|Nuclear

electricity production, nuclear

Oil ST

SE|Electricity|Oil|w/o CCS

Secondary Energy|Electricity|Oil|w/o CCS|1

electricity production, oil

Oil CC

Secondary Energy|Electricity|Oil|w/o CCS|2

electricity production, oil

Oil CC CCS

Secondary Energy|Electricity|Oil|w/ CCS|1

electricity production, at co-generation power plant/oil, post, pipeline 200km, storage 1000m

Oil CHP

Secondary Energy|Electricity|Oil|w/o CCS|3

heat and power co-generation, oil

Oil CHP CCS

Secondary Energy|Electricity|Oil|w/ CCS|2

electricity production, at co-generation power plant/oil, post, pipeline 200km, storage 1000m

Solar CSP

SE|Electricity|Solar|CSP

Secondary Energy|Electricity|Solar|CSP

electricity production, solar thermal parabolic trough, 50 MW

Solar PV Centralized

SE|Electricity|Solar|PV

Secondary Energy|Electricity|Solar|PV|1

electricity production, photovoltaic, commercial

Solar PV Residential

Secondary Energy|Electricity|Solar|PV|2

electricity production, photovoltaic, residential

Wind Onshore

SE|Electricity|Wind|Onshore

Secondary Energy|Electricity|Wind|1

electricity production, wind, <1MW turbine, onshore

Wind Offshore

SE|Electricity|Wind|Offshore

Secondary Energy|Electricity|Wind|2

electricity production, wind, 1-3MW turbine, offshore

Note

IAMs do not necessarily display the same variety of technologies. For example, REMIND does not provide a variable for residential PV production while IMAGE does.

Note

Because of a lack of more diverse inventories, wind power is only represented with relatively small installations (< 1MW, 1-3 MW and >3 MW), in respect to today’s standard. This can lead to overestimate the associated environmental burden.

The table below shows the correspondence between premise, REMIND, IMAGE and LCI terminology, regarding steel and cement producing technologies. The mapping files are available in the library root folder: mappingCement and mappingSteel.

name in premise

name in REMIND

name in IMAGE

name in LCI database

cement

Production|Industry|Cement

Production|Cement

cement production, Portland

steel - primary

Production|Industry|Steel|Primary

Production|Steel|Primary

steel production, converter

steel - secondary

Production|Industry|Steel|Secondary

Production|Steel|Secondary

steel production, electric

The table below shows the correspondence between premise, REMIND, IMAGE and LCI terminology, regarding fuel producing technologies. The mapping file is available in the library root folder: mappingFuels.

Warning

Some fuel types are not properly represented in the LCI database. Available inventories for biomass-based methanol production do not differentiate between wood and grass as the feedstock.

Note

Modelling choice: premise builds several potential supply chains for hydrogen. Because the logistics to supply hydrogen in the future is not known or indicated by the IAM, the choice is made to supply it by truck over 500 km, in a gaseous state.

The production volumes considered for a given scenario can be consulted, like so:

ndb.scenarios[0]["iam data"].production_volumes

To have an updated overview of the mapping concenring all sectors, refer to this file: mapping.

Efficiencies

The efficiency of the different technologies producing commodities (e.g., electricity, steel, cement, fuel) is modelled to change over time by the IAM. premise stores the relative change in efficiency of such technologies.

The table below shows the correspondence between premise, REMIND, IMAGE, regarding efficiency variables for electricity producing technologies. The mapping file is available in the library root folder: mappingElec_.

name in premise

name in REMIND

name in IMAGE

Biomass CHP

Tech|Electricity|Biomass|CHP|w/o CCS|Efficiency

Efficiency|Electricity|Biomass|w/o CCS|3

Biomass CHP CCS

Efficiency|Electricity|Biomass|w/ CCS|2

Biomass ST

Efficiency|Electricity|Biomass|w/o CCS|1

Biomass IGCC CCS

Tech|Electricity|Biomass|IGCCC|w/ CCS|Efficiency

Efficiency|Electricity|Biomass|w/ CCS|1

Biomass IGCC

Tech|Electricity|Biomass|IGCC|w/o CCS|Efficiency

Efficiency|Electricity|Biomass|w/o CCS|2

Coal PC

Tech|Electricity|Coal|PC|w/o CCS|Efficiency

Efficiency|Electricity|Coal|w/o CCS|1

Coal IGCC

Tech|Electricity|Coal|IGCC|w/o CCS|Efficiency

Efficiency|Electricity|Coal|w/o CCS|2

Coal PC CCS

Tech|Electricity|Coal|PCC|w/ CCS|Efficiency

Coal IGCC CCS

Tech|Electricity|Coal|IGCCC|w/ CCS|Efficiency

Efficiency|Electricity|Coal|w/ CCS|1

Coal CHP

Tech|Electricity|Coal|CHP|w/o CCS|Efficiency

Efficiency|Electricity|Coal|w/o CCS|3

Coal CHP CCS

Efficiency|Electricity|Coal|w/ CCS|2

Gas OC

Tech|Electricity|Gas|GT|Efficiency

Efficiency|Electricity|Gas|w/o CCS|1

Gas CC

Tech|Electricity|Gas|CC|w/o CCS|Efficiency

Efficiency|Electricity|Gas|w/o CCS|2

Gas CHP

Tech|Electricity|Gas|CHP|w/o CCS|Efficiency

Efficiency|Electricity|Gas|w/o CCS|3

Gas CHP CCS

Efficiency|Electricity|Gas|w/ CCS|2

Gas CC CCS

Tech|Electricity|Gas|CCC|w/ CCS|Efficiency

Efficiency|Electricity|Gas|w/ CCS|1

Nuclear

Efficiency|Electricity|Nuclear

Oil ST

Tech|Electricity|Oil|DOT|Efficiency

Efficiency|Electricity|Oil|w/o CCS|1

Oil CC

Efficiency|Electricity|Oil|w/o CCS|2

Oil CC CCS

Efficiency|Electricity|Oil|w/ CCS|1

Oil CHP

Efficiency|Electricity|Oil|w/o CCS|3

Oil CHP CCS

Efficiency|Electricity|Oil|w/ CCS|2

The table below shows the correspondence between premise, REMIND, IMAGE, regarding efficiency variables for cement and steel producing technologies. For cement and steel, it is different, as premise derives efficiencies by dividing the the final energy demand by the production volume (to obtain GJ/t steel or cement). This is because efficiency variables for cement and steel is not always given as such. The mapping files are available in the library root folder: mappingCement and mappingSteel.

name in premise

name in REMIND

name in IMAGE

cement

Final Energy|Industry|Cement

FE|Industry|Cement

steel - primary

Final Energy|Industry|Steel

FE|Industry|Steel|Primary

steel - secondary

Final Energy|Industry|Steel|Electricity

FE|Industry|Steel|Secondary

The table below shows the correspondence between premise, REMIND, IMAGE, regarding efficiency variables for fuels producing technologies. The mapping file is available in the library root folder: mappingFuels.

name in premise

name in REMIND

name in IMAGE

biomethane

Tech|Gases|Biomass|w/o CCS|Efficiency

diesel

Tech|Liquids|Oil|Efficiency

gasoline

Tech|Liquids|Oil|Efficiency

diesel, synthetic, wood

Efficiency|Liquids|Biomass|FT Diesel|Woody|w/o CCS

diesel, synthetic, wood, with CCS

Efficiency|Liquids|Biomass|FT Diesel|Woody|w/ CCS

diesel, synthetic, grass

Efficiency|Liquids|Biomass|FT Diesel|Woody|w/o CCS

diesel, synthetic, grass, with CCS

Efficiency|Liquids|Biomass|FT Diesel|Woody|w/ CCS

biodiesel, oil

Tech|Liquids|Biomass|Biofuel|Biodiesel|w/o CCS|Efficiency

Efficiency|Liquids|Biomass|Biodiesel|Oilcrops|w/o CCS

biodiesel, oil, with CCS

Efficiency|Liquids|Biomass|Biodiesel|Oilcrops|w/ CCS

bioethanol, wood

Tech|Liquids|Biomass|Biofuel|Ethanol|Cellulosic|w/o CCS|Efficiency

Efficiency|Liquids|Biomass|Ethanol|Woody|w/o CCS

bioethanol, wood, with CCS

Efficiency|Liquids|Biomass|Ethanol|Woody|w/ CCS

bioethanol, grass

Tech|Liquids|Biomass|Biofuel|Ethanol|Cellulosic|w/o CCS|Efficiency

Efficiency|Liquids|Biomass|Ethanol|Grassy|w/o CCS

bioethanol, grass, with CCS

Efficiency|Liquids|Biomass|Ethanol|Grassy|w/ CCS

bioethanol, grain

Tech|Liquids|Biomass|Biofuel|Ethanol|Conventional|w/o CCS|Efficiency

Efficiency|Liquids|Biomass|Ethanol|Maize|w/o CCS

bioethanol, grain, with CCS

Efficiency|Liquids|Biomass|Ethanol|Maize|w/ CCS

bioethanol, sugar

Tech|Liquids|Biomass|Biofuel|Ethanol|Conventional|w/o CCS|Efficiency

Efficiency|Liquids|Biomass|Ethanol|Sugar|w/o CCS

bioethanol, sugar, with CCS

Efficiency|Liquids|Biomass|Ethanol|Sugar|w/ CCS

methanol, wood

Efficiency|Liquids|Biomass|Methanol|Woody|w/o CCS

methanol, grass

Efficiency|Liquids|Biomass|Methanol|Grassy|w/o CCS

methanol, wood, with CCS

Efficiency|Liquids|Biomass|Methanol|Woody|w/ CCS

methanol, grass, with CCS

Efficiency|Liquids|Biomass|Methanol|Grassy|w/ CCS

premise stores the change in efficiency (called scaling factor) of a given technology relative to 2020. This is based on the fact that the efficiency of ecoinvent datasets are believed to reflect current (2020) efficiency.

Note

If a technology, in a given region, is given a scaling factor of 1.2 in 2030, this means that the corresponding ecoinvent dataset is adjusted so that its efficiency is improved by 20% (by multiplying the dataset inputs by 1/1.2). In other words, premise does not use the efficiency given by the IAM, but rather its change over time relative to 2020.

The scaling factors considered for a given scenario can be consulted, like so:

ndb.scenarios[0]["iam data"].efficiency

Land use and land use change

When building prospective databases using the IAM IMAGE model, the latter provides additional variables relating to average land use and land use change emissions, for each type of crop grown to be used in biofuel production. Upon the creation of biofuel supply chains in the Fuels transformation function, such information is used to adjust the inventories of crop farming datasets. The table below shows the IMAGE variables used to that effect. The mapping file is available in the library root folder: mappingCrops.

Crop family in premise

Crop type in premise

Land use variable in IMAGE [Ha/GJ-Prim]

Land use change variable in IMAGE [kg CO2/GJ-Prim]

sugar

sugarbeet, sugarcane

Land Use|Average|Biomass|Sugar

Emission Factor|CO2|Energy|Supply|Biomass|Average|Sugar

oil

rapeseed, palm oil

Land Use|Average|Biomass|OilCrop

Emission Factor|CO2|Energy|Supply|Biomass|Average|Oilcrops

wood

poplar, eucalyptus

Land Use|Average|Biomass|Woody

Emission Factor|CO2|Energy|Supply|Biomass|Average|Woody

grass

switchgrass, miscanthus

Land Use|Average|Biomass|Grassy

Emission Factor|CO2|Energy|Supply|Biomass|Average|Grassy

grain

corn

Land Use|Average|Biomass|Maize

Emission Factor|CO2|Energy|Supply|Biomass|Average|Maize

The land use and land use change emissions considered for a given scenario can be consulted, like so:

ndb.scenarios[0]["iam data"].land_use
ndb.scenarios[0]["iam data"].land_use_change

Carbon Capture and Storage

Some scenarios involve the capture and storage of CO2 emissions of certain sectors (e.g., cement and steel). The capture rate of a given sector is calculated from the IAM data file, as:

rate = amount of CO2 captured / (amount of CO2 captured + amount of CO2 not captured)

The table below lists the variables needed to calculate those rates.

name in premise

name in REMIND

name in IMAGE

cement - CO2 (not captured)

Emi|CO2|FFaI|Industry|Cement

Emissions|CO2|Industry|Cement|Gross

cement - CCO2 (captured)

Emi|CCO2|FFaI|Industry|Cement

Emissions|CO2|Industry|Cement|Sequestered

steel - CO2 (not captured)

Emi|CO2|FFaI|Industry|Steel

Emissions|CO2|Industry|Steel|Gross

steel - CCO2 (captured)

Emi|CCO2|FFaI|Industry|Steel

Emissions|CO2|Industry|Steel|Sequestered

The carbon capture rates which are floating values comprised between 0 and 1, can be consulted like so:

ndb.scenarios[0]["iam data"].carbon_capture_rate

Data sources external to the IAM

premise tries to adhere to the IAM scenario data as much as possible. There are however a number of cases where external data sources are used. This is notably the case for non-CO2 pollutants emissions for different sectors (electricity, steel and cement), as well as expected efficiency gains for photovoltaic panels.

Air emissions

premise relies on projections from the air emissions models GAINS-EU and GAINS-IAM to adjust the emissions of pollutants for different sectors. As with efficiencies, premise stores the change in emissions (called scaling factor) of a given technology relative to 2020. This is based on the fact that the emissions of ecoinvent datasets are believed to reflect the current (2020) situation. Hence, if a technology, in a given region, has a scaling factor of 1.2 in 2030, this means that the corresponding ecoinvent dataset is adjusted so that its emissions of a given substance is improved by 20%. In other words, premise does not use the emissions level given by GAINS, but rather its change over time relative to 2020.

For more information about this step, refer to sub-section “GAINS emission factors” in the EXTRACT section.

Photovoltaic panels

Module efficiencies in 2010 for micro-Si and single-Si are from IEA_ Task 12 report. For multi-Si, CIGS, CIS and CdTe, they are from IEA2 road map report on PV panels.

Current (2020) module efficiencies for all PV types are given by a 2021 report from the Fraunhofer Institute.

The efficiencies indicated for 2050 are what has been obtained in laboratory conditions by the Fraunhofer Institute. In other words, it is assumed that by 2050, solar PVs will reach production level efficiencies equal to those observed today in laboratories.

% module efficiency

micro-Si

single-Si

multi-Si

CIGS

CIS

CdTe

2010

10

15.1

14

11

11

10

2020

11.9

17.9

16.8

14

14

16.8

2050

12.5

26.7

24.4

23.4

23.4

21

TRANSFORM

A series of transformations are applied to the Life Cycle Inventory (LCI) database to align process performance and technology market shares with the outputs from the Integrated Assessment Model (IAM) scenario.

Biomass

Run

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
    scenarios=[
            {"model":"remind", "pathway":"SSP2-Base", "year":2028}
        ],
    source_db="ecoinvent 3.7 cutoff",
    source_version="3.7.1",
    key='xxxxxxxxxxxxxxxxxxxxxxxxx'
)
ndb.update("biomass")

Regional biomass markets

premise creates regional markets for biomass which is meant to be used as fuel in biomass-fired powerplants or heat generators. Originally in ecoinvent, the biomass being supplied to biomass-fired powerplants is “purpose grown” biomass that originate forestry activities (called “market for wood chips” in ecoinvent). While this type of biomass is suitable for such purpose, it is considered a co-product of the forestry activity, and bears a share of the environmental burden of the process it originates from (notably the land footprint, emissions, potential use of chemicals, etc.).

However, not all the biomass projected to be used in IAM scenarios is “purpose grown”. In fact, significant shares are expected to originate from forestry residues. In such cases, the environmental burden of the forestry activity is entirely allocated to the determining product (e.g., timber), not to the residue, which comes “free of burden”.

Hence, premise creates average regional markets for biomass, which represents the average shares of “purpose grown” and “residual” biomass being fed to biomass-fired powerplants.

The following market is created for each IAM region:

market name

location

market for biomass, used as fuel

all IAM regions

inside of which, the shares of “purpose grown” and “residual” biomass is represented by the following activities:

name in premise

name in REMIND

name in IMAGE

name in LCI database

biomass - purpose grown

SE|Electricity|Biomass|Energy Crops

Primary Energy|Biomass|Energy Crops

market for wood chips

biomass - residual

SE|Electricity|Biomass|Residues

Primary Energy|Biomass|Residues

supply of forest residue

The sum of those shares equal 1. The activity “supply of forest residue” includes the energy, embodied biogenic CO2, transport and associated emissions to chip the residual biomass and transport it to the powerplant, but no other forestry-related burden is included.

Note

You can check the share of residual biomass used for power generation assumed in your scenarios by generating a scenario summary report.

Note

When running premise with the consequential method, the biomass market is only composed of purpose-grown biomass. This is because the residual biomass cannot be considered a marginal supplier for an increase in demand for biomass.

ndb.generate_scenario_report()

Power generation

Run

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
    scenarios=[
            {"model":"remind", "pathway":"SSP2-Base", "year":2028}
        ],
    source_db="ecoinvent 3.7 cutoff",
    source_version="3.7.1",
    key='xxxxxxxxxxxxxxxxxxxxxxxxx'
)
ndb.update("electricity")

The energy conversion efficiency of power plant datasets for specific technologies is adjusted to align with the efficiency changes indicated by the IAM scenario. Two approaches are posisble: * application of a scaling factor to the inputs of the dataset relative to the current efficiency * application of a scaling factor to the inputs of the dataset to match the absolute efficiency given by the IAM scenario

The first approach (default) preserves

Combustion-based powerplants

First, premise adjust the efficiency of coal- and lignite-fired power plants on the basis of the excellent work done by Oberschelp et al. (2019), to update some datasets in ecoinvent, which are, for some of them, several decades old. More specifically, the data provides plant-specific efficiency and emissions factors. We average them by country and fuel type to obtain volume-weighted factors. The efficiency of the following datasets is updated:

  • electricity production, hard coal

  • electricity production, lignite

  • heat and power co-generation, hard coal

  • heat and power co-generation, lignite

The data from Oberschelp et al. (2019) also allows us to update emissions of SO2, NOx, CH4, and PMs.

Second, premise iterates through coal, lignite, natural gas, biogas, and wood-fired power plant datasets in the LCI database to calculate their current efficiency (i.e., the ratio between the primary fuel energy entering the process and the output energy produced, which is often 1 kWh). If the IAM scenario anticipates a change in efficiency for these processes, the inputs of the datasets are scaled up or down by the scaling factor to effectively reflect a change in fuel input per kWh produced.

The origin of this scaling factor is the IAM scenario selected.

To calculate the old and new efficiency of the dataset, it is necessary to know the net calorific content of the fuel. The table below shows the Lower Heating Value for the different fuels used in combustion-based power plants.

name of fuel

LHV [MJ/kg, as received]

hard coal

26.7

lignite

11.2

petroleum coke

31.3

wood pellet

16.2

wood chips

18.9

natural gas

45

gas, natural, in ground

45

refinery gas

50.3

propane

46.46

heavy fuel oil

38.5

oil, crude, in ground

38.5

light fuel oil

42.6

biogas

22.73

biomethane

47.5

waste

14

methane, fossil

47.5

methane, biogenic

47.5

methane, synthetic

47.5

diesel

43

gasoline

42.6

petrol, 5% ethanol

41.7

petrol, synthetic, hydrogen

42.6

petrol, synthetic, coal

42.6

diesel, synthetic, hydrogen

43

diesel, synthetic, coal

43

diesel, synthetic, wood

43

diesel, synthetic, wood, with CCS

43

diesel, synthetic, grass

43

diesel, synthetic, grass, with CCS

43

hydrogen, petroleum

120

hydrogen, electrolysis

120

hydrogen, biomass

120

hydrogen, biomass, with CCS

120

hydrogen, coal

120

hydrogen, from natural gas

120

hydrogen, from natural gas, with CCS

120

hydrogen, biogas

120

hydrogen, biogas, with CCS

120

hydrogen

120

biodiesel, oil

38

biodiesel, oil, with CCS

38

bioethanol, wood

26.5

bioethanol, wood, with CCS

26.5

bioethanol, grass

26.5

bioethanol, grass, with CCS

26.5

bioethanol, grain

26.5

bioethanol, grain, with CCS

26.5

bioethanol, sugar

26.5

bioethanol, sugar, with CCS

26.5

ethanol

26.5

methanol, wood

19.9

methanol, grass

19.9

methanol, wood, with CCS

19.9

methanol, grass, with CCS

19.9

liquified petroleum gas, natural

45.5

liquified petroleum gas, synthetic

45.5

uranium, enriched 3.8%, in fuel element for light water reactor

4199040

nuclear fuel element, for boiling water reactor, uo2 3.8%

4147200

nuclear fuel element, for boiling water reactor, uo2 4.0%

4147200

nuclear fuel element, for pressure water reactor, uo2 3.8%

4579200

nuclear fuel element, for pressure water reactor, uo2 4.0%

4579200

nuclear fuel element, for pressure water reactor, uo2 4.2%

4579200

uranium hexafluoride

709166

enriched uranium, 4.2%

4579200

mox fuel element

4579200

heat, from hard coal

1

heat, from lignite

1

heat, from petroleum coke

1

heat, from wood pellet

1

heat, from natural gas, high pressure

1

heat, from natural gas, low pressure

1

heat, from heavy fuel oil

1

heat, from light fuel oil

1

heat, from biogas

1

heat, from waste

1

heat, from methane, fossil

1

heat, from methane, biogenic

1

heat, from diesel

1

heat, from gasoline

1

heat, from bioethanol

1

heat, from biodiesel

1

heat, from liquified petroleum gas, natural

1

heat, from liquified petroleum gas, synthetic

1

bagasse, from sugarcane

15.4

bagasse, from sweet sorghum

13.8

sweet sorghum stem

4.45

cottonseed

21.97

flax husks

21.5

coconut husk

20

sugar beet pulp

5.11

cleft timber

14.46

rape meal

31.1

molasse, from sugar beet

16.65

sugar beet

4.1

barkey grain

19.49

rye grain

12

sugarcane

5.3

palm date

10.8

whey

1.28

straw

15.5

grass

17

manure, liquid

0.875

manure, solid

3.6

kerosene, from petroleum

43

kerosene, synthetic, from electrolysis, energy allocation

43

kerosene, synthetic, from electrolysis, economic allocation

43

kerosene, synthetic, from coal, energy allocation

43

kerosene, synthetic, from coal, economic allocation

43

kerosene, synthetic, from natural gas, energy allocation

43

kerosene, synthetic, from natural gas, economic allocation

43

kerosene, synthetic, from biomethane, energy allocation

43

kerosene, synthetic, from biomethane, economic allocation

43

kerosene, synthetic, from biomass, energy allocation

43

kerosene, synthetic, from biomass, economic allocation

43

Additionally, the biogenic and fossil CO2 emissions of the datasets are also scaled up or down by the same factor, as they are proportional to the amount of fuel used.

Below is an example of a natural gas power plant with a current (2020) conversion efficiency of 77%. If the IAM scenario indicates a scaling factor of 1.03 in 2030, this suggests that the efficiency increases by 3% relative to the current level. As shown in the table below, this would result in a new efficiency of 79%, where all inputs, as well as CO2 emissions outputs, are re-scaled by 1/1.03 (=0.97).

While non-CO2 emissions (e.g., CO) are reduced because of the reduction in fuel consumption, the emission factor per energy unit remains the same (i.e., gCO/MJ natural gas)). It can be re-scaled using the .update(“emissions”) function, which updates emission factors according to GAINS projections.

electricity production, natura gas, conventional

before

after

unit

electricity production

1

1

kWh

natural gas

0.1040

0.1010

m3

water

0.0200

0.0194

m3

powerplant construction

1.00E-08

9.71E-09

unit

CO2, fossil

0.0059

0.0057

kg

CO, fossil

5.87E-06

5.42E-03

kg

fuel-to-electricity efficiency

77%

79%

%

premise has a couple of rules regarding projected scaling factors:

  • scaling factors inferior to 1 beyond 2020 are not accepted and are treated as 1.

  • scaling factors superior to 1 before 2020 are not accepted and are treated as 1.

  • efficiency can only improve over time.

This is to prevent degrading the performance of a technology in the future, or improving its performance in the past, relative to today.

Note

You can check the efficiencies assumed in your scenarios by generating a scenario summary report, or a report of changes. They are automatically generated after each database export, but you can also generate them manually:

ndb.generate_scenario_report()
ndb.generate_change_report()

Photovoltaics panels

Photovoltaic panels are expected to improve over time. The following module efficiencies are considered for the different types of PV panels:

% module efficiency

micro-Si

single-Si

multi-Si

CIGS

CIS

CdTe

2010

10

15.1

14

11

11

10

2020

11.9

17.9

16.8

14

14

16.8

2050

12.5

26.7

24.4

23.4

23.4

21

The sources for these efficiencies are given in the inventory file LCI_PV:

Given a scenario year, premise iterates through the different PV panel installation datasets to update their efficiency accordingly. To do so, the required surface of panel (in m2) per kW of capacity is adjusted down (or up, if the efficiency is lower than current).

To calculate the current efficiency of a PV installation, premise assumes a solar irradiation of 1000 W/m2. Hence, the current efficiency is calculated as:

current_eff [%] = installation_power [W]  / (panel_surface [m2] * 1000 [W/m2])

The scaling factor is calculated as:

scaling_factor = current_eff / new_eff

The required surface of PV panel in the dataset is then adjusted like so:

new_surface = current_surface * (1 / scaling_factor)

For scenario years beyond 2050, 2050 efficiency values are used.

The table below provides such an example where a 450 kWp flat-roof installation sees its current (2020) module efficiency improving from 20% to 26% by 2050. THe are of PV panel (and mounting system) has been multiplied by 1 / (0.26/0.20), all other inputs remaining unchanged.

450kWp flat roof installation

before

after

unit

photovoltaic flat-roof installation, 450 kWp, single-SI, on roof

1

1

unit

inverter production, 500 kW

1.5

1.5

unit

photovoltaic mounting system, …

2300

1731

m2

photovoltaic panel, single-SI

2500

1881

m2

treatment, single-SI PV module

30000

30000

kg

electricity, low voltage

25

25

kWh

module efficiency

20%

26%

%

Markets

premise creates additional datasets that represent the average supply and production pathway for a given commodity for a given scenario, year and region.

Such datasets are called regional markets. Hence, a regional market for high voltage electricity contains the different technologies that supply electricity at high voltage in a given IAM region, in proportion to their respective production volumes.

Regional electricity markets

premise creates high, medium and low-voltage electricity markets for each IAM region. It starts by creating high-voltage markets and define the share of each supplying technology by their respective production volumes in respect to the total volume produced.

High voltage supplying technologies are all technologies besides:

  • residential (<=3kWp) photovoltaic power (low voltage)

  • waste incineration co-generating powerplants (medium voltage)

Several datasets can qualify for a given technology, in a given IAM region. To define to which extent a given dataset should be supplying in the market, premise uses the current production volume of the dataset.

For example, if coal-fired powerplants are to supply 25% of the high voltage electricity in the IAM region “Europe”, premise fetches the production volumes of all coal-fired powerplants which ecoinvent location is included in the IAM region “Europe” (e.g., DE, PL, LT, etc.), and allocates to each of those a supply share based on their respective production volume in respect to the total production volume of coal-fired powerplants.

For example, the table below shows the contribution of biomass-fired CHP powerplants in the regional high voltage electricity market for IMAGE’s “WEU” region (Western Europe). The biomass CHP technology represents 2.46% of the supply mix. Biomass CHP datasets included in the region “WEU” are given a supply share corresponding to their respective current production volumes.

energy type

Supplier name

Supplier location

Contribution within energy type

Final contribution

Biomass CHP

heat and power co-generation, wood chips

FR

3.80%

0.09%

Biomass CHP

heat and power co-generation, wood chips

AT

2.87%

0.07%

Biomass CHP

heat and power co-generation, wood chips

NO

0.06%

0.00%

Biomass CHP

heat and power co-generation, wood chips

FI

7.65%

0.19%

Biomass CHP

heat and power co-generation, wood chips

SE

9.04%

0.22%

Biomass CHP

heat and power co-generation, wood chips

IT

8.27%

0.20%

Biomass CHP

heat and power co-generation, wood chips

BE

4.59%

0.11%

Biomass CHP

heat and power co-generation, wood chips

DE

12.53%

0.31%

Biomass CHP

heat and power co-generation, wood chips

LU

0.05%

0.00%

Biomass CHP

heat and power co-generation, wood chips

DK

6.60%

0.16%

Biomass CHP

heat and power co-generation, wood chips

GR

0.01%

0.00%

Biomass CHP

heat and power co-generation, wood chips

CH

1.81%

0.04%

Biomass CHP

heat and power co-generation, wood chips

ES

5.10%

0.13%

Biomass CHP

heat and power co-generation, wood chips

PT

1.34%

0.03%

Biomass CHP

heat and power co-generation, wood chips

IE

0.77%

0.02%

Biomass CHP

heat and power co-generation, wood chips

NL

2.32%

0.06%

Biomass CHP

heat and power co-generation, wood chips

GB

33.18%

0.81%

_

_

Sum

100.00%

2.46%

Transformation losses are added to the high-voltage market datasets. Transformation losses are the result of weighting country-specific high voltage losses (provided by ecoinvent) of countries included in the IAM region with their respective current production volumes (also provided by ecoinvent). This is not ideal as it supposes that future country-specific production volumes will remain the same in respect to one another.

Storage

If the IAM scenario requires the use of storage, premise adds a storage dataset to the high voltage market. premise can add two types of storage:

  • storage via a large-scale flow battery (electricity supply, high voltage, from vanadium-redox flow battery system)

  • storage via the conversion of electricity to hydrogen and subsequent use in a gas turbine (electricity production, from hydrogen-fired one gigawatt gas turbine)

The electricity storage via battery incurs a 33% loss. It is operated by a 8.3 MWh vanadium redox-based flow battery, with a lifetime of 20 years or 8176 cycle-lifes (i.e., 49,000 MWh).

The storage of electricity via hydrogen is done in two steps: first, the electricity is converted to hydrogen via a 1MW PEM electrolyser, with an efficiency of 62%. The hydrogen is then stored in a geological cavity and used in a gas turbine, with an efficiency of 51%. Accounting for leakages and losses, the overall efficiency of the process is about 37% (i.e., 2.7 kWh necessary to deliver 1 kWh to the grid).

The efficiency of the H2-fed gas turbine is based on the parameters of Ozawa et al. (2019).

The workflow is not too different from that of high voltage markets. There are however only two possible providers of electricity in medium voltage markets: the high voltage market, as well as waste incineration powerplants.

High-to-medium transformation losses are added as an input of the medium voltage market to itself. Distribution losses are modelled the same way as for high voltage markets and are added to the input from high voltage market.

Low voltage regional markets receive an input from the medium voltage market, as well as from residential photovoltaic power.

Medium-to-low transformation losses are added as an input from the low voltage market to itself. Distribution losses are modelled the same way as for high and medium voltage markets, and are added to the input from the medium voltage market.

The table below shows the example of a low voltage market for the IAM IMAGE regional “WEU”.

supplier

amount

unit

location

description

market group for electricity, medium voltage

1.023880481

kilowatt hour

WEU

input from medium voltage + distribution losses

market group for electricity, low voltage

0.025538286

kilowatt hour

WEU

transformation losses (2.55%)

electricity production, photovoltaic, residential

0.00035691

kilowatt hour

DE

electricity production, photovoltaic, residential

0.000143875

kilowatt hour

IT

electricity production, photovoltaic, residential

9.38E-05

kilowatt hour

ES

electricity production, photovoltaic, residential

9.03E-05

kilowatt hour

GB

electricity production, photovoltaic, residential

7.82E-05

kilowatt hour

FR

electricity production, photovoltaic, residential

6.80E-05

kilowatt hour

NL

electricity production, photovoltaic, residential

3.76E-05

kilowatt hour

BE

electricity production, photovoltaic, residential

2.16E-05

kilowatt hour

GR

electricity production, photovoltaic, residential

2.08E-05

kilowatt hour

CH

electricity production, photovoltaic, residential

1.48E-05

kilowatt hour

AT

electricity production, photovoltaic, residential

9.44E-06

kilowatt hour

SE

electricity production, photovoltaic, residential

8.66E-06

kilowatt hour

DK

electricity production, photovoltaic, residential

6.83E-06

kilowatt hour

PT

electricity production, photovoltaic, residential

2.60E-06

kilowatt hour

FI

electricity production, photovoltaic, residential

1.30E-06

kilowatt hour

LU

electricity production, photovoltaic, residential

1.01E-06

kilowatt hour

NO

electricity production, photovoltaic, residential

2.40E-07

kilowatt hour

IE

distribution network construction, electricity, low voltage

8.74E-08

kilometer

RoW

market for sulfur hexafluoride, liquid

2.99E-09

kilogram

RoW

sulfur hexafluoride

2.99E-09

kilogram

transformer emissions

Note

You can check the electricity supply mixes assumed in your scenarios by generating a scenario summary report.

ndb.generate_scenario_report()

Long-term regional electricity markets

Long-term (i.e., 20, 40 and 60 years) regional markets are created for modelling the lifetime-weighted burden associated to electricity supply for systems that have a long lifetime (e.g., battery electric vehicles, buildings).

These long-term markets contain a period-weighted electricity supply mix. For example, if the scenario year is 2030 and the period considered is 20 years, the supply mix represents the supply mixes between 2030 and 2050, with an equal weight given to each year.

The rest of the modelling is similar to that of regular regional electricity markets described above.

Market datasets originally present in the ecoinvent LCI database are cleared from any inputs. Instead, an input from the newly created regional market is added, depending on the location of the dataset.

The table below shows the example of the low voltage electricity market for Great Britain, which now only includes an input from the “WEU” regional market, which “includes” it in terms of geography.

Output

_

_

_

producer

amount

unit

location

market for electricity, low voltage

1.00E+00

kilowatt hour

GB

Input

_

_

_

supplier

amount

unit

location

market group for electricity, low voltage

1.00E+00

kilowatt hour

WEU

Once the new markets are created, premise re-links all electricity-consuming activities to the new regional markets. The regional market it re-links to depends on the location of the consumer.

Cement production

The modelling of future improvements in the cement sector is relatively simple at the moment, and does not involve the emergence of new technologies (e.g., electric kilns).

Run

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
    scenarios=[
            {"model":"remind", "pathway":"SSP2-Base", "year":2028}
        ],
    source_db="ecoinvent 3.7 cutoff",
    source_version="3.7.1",
    key='xxxxxxxxxxxxxxxxxxxxxxxxx'
)
ndb.update("cement")

premise duplicates clinker production datasets in ecoinvent (called “clinker production”) so as to create a proxy dataset for each IAM region. The location of the proxy datasets used for a given IAM region is a location included in the IAM region. If no valid dataset is found, premise resorts to using a rest-of-the-world (RoW) dataset to represent the IAM region.

premise changes the location of these duplicated datasets and fill in different fields, such as that of production volume.

premise then adjusts the thermal efficiency of the process. It does so by calculating the technology-weighted energy requirements per ton of clinker. Based on GNR/IEA roadmap data, premise uses:

  • the share of kiln technology for a given region today (2020):
    • wet,

    • dry,

    • dry with pre-heater,

    • and dry with pre-heater and pre-calciner

  • the energy requirement for each of these technologies today (2020).

Once the energy required per ton clinker today (2020) is known, it is multiplied by a scaling factor that represents a change in efficiency between today and the scenario year.

Note

You can check the efficiency gains assumed relative to 2020 in your scenarios by generating a scenario summary report.

ndb.generate_scenario_report()

Note

premise enforces a lower limit on the fuel consumption per ton of clinker. This limit is set to 2.8 GJ/t clinker and corresponds to the minimum theoretical fuel consumption with an moisture content of the raw materials, as considered in the 2018 IEA cement roadmap report. Hence, regardless of the scaling factor, the fuel consumption per ton of clinker will never be less than 2.8 GJ/t.

Once the new energy input is determined, premise scales down the fuel, and the fossil and biogenic CO2 emissions accordingly, based on the Lower Heating Value and CO2 emission factors for these fuels.

Note that the change in CO2 emissions only concerns the share that originates from the combustion of fuels. It does not concern the calcination emissions due to the production of calcium oxide (CaO) from calcium carbonate (CaCO3), which is set at a fix emission rate of 525 kg CO2/t clinker.

If the IAM scenario indicates that a share of the CO2 emissions for the cement sector in a given region and year is sequestered and stored, premise adds CCS to the corresponding clinker production dataset.

The CCS dataset used to that effect is from Meunier et al., 2020. The dataset described the capture of CO2 from a cement plant. To that dataset, premise adds another dataset that models the storage of the CO2 underground, from Volkart et al, 2013.

Besides electricity, the CCS process requires heat, water and others inputs to regenerate the amine-based sorbent. We use two data points to approximate the heat requirement: 3.66 MJ/kg CO2 captured in 2020, and 2.6 MJ/kg in 2050. The first number is from Meunier et al., 2020, while the second number is described as the best-performing pilot project today, according to the 2022 review of pilot projects by the Global CCS Institute. It is further assumed that the heat requirement is fulfilled to an extent of 15% by the recovery of excess heat, as mentioned in the 2018 IEA cement roadmap report.

Note

You can check the the carbon capture rate for cement production assumed in your scenarios by generating a scenario summary report.

ndb.generate_scenario_report()

Run

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
    scenarios=[
            {"model":"remind", "pathway":"SSP2-Base", "year":2028}
        ],
    source_db="ecoinvent 3.7 cutoff",
    source_version="3.7.1",
    key='xxxxxxxxxxxxxxxxxxxxxxxxx'
)
ndb.update("cement")

When clinker production datasets are created for each IAM region, premise duplicates cement production datasets for each IAM region as well. These cement production datasets link the newly created clinker production dataset, corresponding to their IAM region.

premise used to modify the composition of cement markets to reflect a lower clinker content over time, based on external projections. This is no longer performed, as it is not an assumption stemming from the IAM model, but rather a projection of the cement industry.

Market datasets originally present in the ecoinvent LCI database are cleared from any inputs. Instead, an input from the newly created regional market is added, depending on the location of the dataset.

The table below shows the example of the clinker market for South Africa, which now only includes an input from the “SAF” regional market, which “includes” it in terms of geography.

Output

_

_

_

producer

amount

unit

location

market for clinker

1.00E+00

kilogram

ZA

Input

_

_

_

supplier

amount

unit

location

market for clinker

1.00E+00

kilogram

*SAF

Once cement production and market datasets are created, premise re-links cement-consuming activities to the new regional markets for cement. The regional market it re-links to depends on the location of the consumer.

Steel production

Run

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
    scenarios=[
            {"model":"remind", "pathway":"SSP2-Base", "year":2028}
        ],
    source_db="ecoinvent 3.7 cutoff",
    source_version="3.7.1",
    key='xxxxxxxxxxxxxxxxxxxxxxxxx'
)
ndb.update("steel")"

The modelling of future improvements in the steel sector is relatively simple at the moment, and does not involve the emergence of new technologies (e.g., hydrogen-based DRI, electro-winning).

premise duplicates steel production datasets in ecoinvent for the production of primary and secondary steel (called respectively “steel production, converter” and “steel production, electric”) so as to create a proxy dataset for each IAM region.

The location of the proxy datasets used for a given IAM region is a location included in the IAM region. If no valid dataset is found, premise resorts to using a rest-of-the-world (RoW) dataset to represent the IAM region.

premise changes the location of these duplicated datasets and fill in different fields, such as that of production volume.

Regarding primary steel production (using BO-BOF), premise adjusts the inputs of fuels found in:

  • the pig iron production datasets,

  • the steel production datasets,

assuming an integrated steel mill unit, by multiplying these fuel inputs by a scaling factor provided by the IAM scenario.

Typical fuel inputs for these process are natural gas, coal, coal-based coke. Emissions of (fossil) CO2 are scaled accordingly.

Regarding the production of secondary steel (using EAF), premise adjusts the input of electricity based on the scaling factor provided by the IAM scenario.

Note

You can check the efficiency gains assumed relative to 2020 for steel production in your scenarios by generating a scenario summary report.

ndb.generate_scenario_report()

Warning

If your system of interest relies heavily on the provision of steel, you should probably consider modelling steel production based on primary data. ecoinvent datasets for steel production rely on a few data points, which are then further process transformed by premise. Therefore, there is a large modelling uncertainty.

If the IAM scenario indicates that a share of the CO2 emissions from the steel sector in a given region and year is sequestered and stored, premise adds a corresponding input from a CCS dataset. The datatset used to that effect is from Meunier et al., 2020. The dataset described the capture of CO2 from a cement plant, not a steel mill, but it is assumed to be an acceptable approximation since the CO2 concentration in the flue gases should not be significantly different.

To that dataset, premise adds another dataset that models the storage of the CO2 underground, from Volkart et al, 2013.

Besides electricity, the CCS process requires heat, water and others inputs to regenerate the amine-based sorbent. We use two data points to approximate the heat requirement: 3.66 MJ/kg CO2 captured in 2020, and 2.6 MJ/kg in 2050. The first number is from Meunier et al., 2020, while the second number is described as the best-performing pilot project today, according to the 2022 review of pilot projects by the Global CCS Institute. It is further assumed that the heat requirement is fulfilled to an extent of 15% by the recovery of excess heat, as mentioned in the 2018 IEA cement roadmap report, which is assumed to be also valid in the case of a steel mill.

premise create a dataset “market for steel, low-alloyed” for each IAM region. Within each dataset, the supply shares of primary and secondary steel are adjusted to reflect the projections from the IAM scenario, for a given region and year, based on the variables below.

name in premise

name in REMIND

name in IMAGE

name in LCI database

steel - primary

Production|Industry|Steel|Primary

Production|Steel|Primary

steel production, converter

steel - secondary

Production|Industry|Steel|Secondary

Production|Steel|Secondary

steel production, electric

The table below shows an example of the market for India, where 66% of the steel comes from an oxygen converter process (primary steel), while 34% comes from an electric arc furnace process (secondary steel).

Output

_

_

_

producer

amount

unit

location

market for steel, low-alloyed

1

kilogram

IND

Input

supplier

amount

unit

location

market group for transport, freight, inland waterways, barge

0.5

ton kilometer

GLO

market group for transport, freight train

0.35

ton kilometer

GLO

market for transport, freight, sea, bulk carrier for dry goods

0.38

ton kilometer

GLO

transport, freight, lorry, unspecified, regional delivery

0.12

ton kilometer

IND

steel production, converter, low-alloyed

0.66

kilogram

IND

steel production, electric, low-alloyed

0.34

kilogram

IND

Market datasets originally present in the ecoinvent LCI database are cleared from any inputs. Instead, an input from the newly created regional market is added, depending on the location of the dataset.

The table below shows the example of the clinker market for South Africa, which now only includes an input from the “SAF” regional market, which “includes” it in terms of geography.

Output

_

_

_

producer

amount

unit

location

market for clinker

1.00E+00

kilogram

ZA

Input

_

_

_

supplier

amount

unit

location

market for clinker

1.00E+00

kilogram

SAF

Once steel production and market datasets are created, premise re-links steel-consuming activities to the new regional markets for steel. The regional market it re-links to depends on the location of the consumer.

Transport

Run

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
    scenarios=[
            {"model":"remind", "pathway":"SSP2-Base", "year":2028}
        ],
    source_db="ecoinvent 3.7 cutoff",
    source_version="3.7.1",
    key='xxxxxxxxxxxxxxxxxxxxxxxxx'
)
ndb.update("two_wheelers")
ndb.update("cars")
ndb.update("trucks")
ndb.update("buses")

premise imports inventories for transport activity operated by:

  • two-wheelers

  • passenger cars

  • medium and heavy duty trucks

  • buses

These inventories are available for the construction year of 2000 to 2050, by steps of 5 years, but premise only imports vehicles with a construction year inferior or equal to the scenario year (vehicle from 2050 will not be imported in a database for the scenario year of 2030, but vehicles from 2020 will, as they are necessary to build the fleet average vehicles).

The following size classes of medium and heavy duty trucks are imported:

  • 3.5t

  • 7.5t

  • 18t

  • 26t

  • 40t

These weights refer to the vehicle gross mass (the maximum weight the vehicle is allowed to reach, fully loaded).

Each truck is available for a variety of powertrain types:

  • fuel cell electric

  • battery electric

  • diesel hybrid

  • plugin diesel hybrid

  • diesel

  • compressed gas

but also for different driving cycles, to which a range autonomy of the vehicle is associated:

  • urban delivery (required range autonomy of 150 km)

  • regional delivery (required range autonomy of 400 km)

  • long haul (required range autonomy of 800 km)

Those are driving cycles developed for the software VECTO, which have become standard in measuring the CO2 emissions of trucks.

The truck vehicle model is from Sacchi et al, 2021.

Note

Not all powertrain types are available for regional and long haul driving cycles. This is specifically the case for battery electric trucks, for which the mass and size prevent them from completing the cycle, or surpasses the vehicle gross weight.

Warning

A consequence of replacing original truck datasets with those provided by premise may be a steep increase in CO2-eq. emissions, especially if the urban driving cycle is chosen. Overall, considering and size classes, diesel truck datasets from ecoinvent have lower fuel consumption and exhaust emissions.

Fleet average trucks

REMIND and IMAGE provide fleet composition data, per scenario, region and year.

The fleet data is expressed in “vehicle-kilometer” performed by each type of vehicle, in a given region and year.

premise uses the following loads to translate the transport demand from “vehicle-kilometers” to “ton-kilometers”, derived from TRACCS:

load [tons]

urban delivery

regional delivery

long haul

3.5t

0.26

0.26

0.8

7.5t

0.52

0.52

1.6

18t

1.35

1.35

4.1

26t

2.05

2.05

6.2

32t

6.1

6.1

9.1

40t

6.1

6.1

9.1

Note

Loads from the TRACCS survey data are representative for EU-28 conditions. premise applies these loads to all IAM regions. Hence, there might be some inconsistency at this level. Also, these loads are much lower than those assumed in original ecoinvent truck datasets.

premise uses the fleet data to produce fleet average trucks for each IAM region, and more specifically:

  • a fleet average truck, all powertrains and size classes considered

  • a fleet average truck, all powertrains considered, for a given size class

They appear in the LCI database as the following:

truck transport dataset name

description

transport, freight, lorry, 3.5t gross weight, unspecified powertrain, long haul

fleet average, for 3.5t size class, long haul cycle

transport, freight, lorry, 3.5t gross weight, unspecified powertrain, regional delivery

fleet average, for 3.5t size class, regional delivery cycle

transport, freight, lorry, 3.5t gross weight, unspecified powertrain, urban delivery

fleet average, for 3.5t size class, urban delivery cycle

transport, freight, lorry, 7.5t gross weight, unspecified powertrain, long haul

fleet average, for 7.5t size class, long haul cycle

transport, freight, lorry, 7.5t gross weight, unspecified powertrain, regional delivery

fleet average, for 7.5t size class, regional delivery cycle

transport, freight, lorry, 7.5t gross weight, unspecified powertrain, urban delivery

fleet average, for 7.5t size class, urban delivery cycle

transport, freight, lorry, 18t gross weight, unspecified powertrain, long haul

fleet average, for 18t size class, long haul cycle

transport, freight, lorry, 18t gross weight, unspecified powertrain, regional delivery

fleet average, for 18t size class, regional delivery cycle

transport, freight, lorry, 18t gross weight, unspecified powertrain, urban delivery

fleet average, for 18t size class, urban delivery cycle

transport, freight, lorry, 26t gross weight, unspecified powertrain, long haul

fleet average, for 26t size class, long haul cycle

transport, freight, lorry, 26t gross weight, unspecified powertrain, regional delivery

fleet average, for 26t size class, regional delivery cycle

transport, freight, lorry, 26t gross weight, unspecified powertrain, urban delivery

fleet average, for 26t size class, urban delivery cycle

transport, freight, lorry, 40t gross weight, unspecified powertrain, long haul

fleet average, for 26t size class, long haul cycle

transport, freight, lorry, 40t gross weight, unspecified powertrain, regional delivery

fleet average, for 26t size class, regional delivery cycle

transport, freight, lorry, 40t gross weight, unspecified powertrain, urban delivery

fleet average, for 26t size class, urban delivery cycle

transport, freight, lorry, unspecified, long haul

fleet average, all powertrain types, all size classes

transport, freight, lorry, unspecified, regional delivery

fleet average, all powertrain types, all size classes

transport, freight, lorry, unspecified, urban delivery

fleet average, all powertrain types, all size classes

Relinking

Regarding trucks, premise re-links truck transport-consuming activities to the newly created fleet average truck datasets.

The following table shows the correspondence between the original truck transport datasets and the new ones replacing them:

Original dataset

Replaced by (REMIND)

Replaced by (IMAGE)

transport, freight, lorry, unspecified

transport, freight, lorry, unspecified

transport, freight, lorry, unspecified

transport, freight, lorry 16-32 metric ton

transport, freight, lorry, 26t gross weight, unspecified powertrain

transport, freight, lorry, 26t gross weight, unspecified powertrain

transport, freight, lorry 28 metric ton, fatty acid methyl ester 100%

transport, freight, lorry, 26t gross weight, unspecified powertrain

transport, freight, lorry, 26t gross weight, unspecified powertrain

transport, freight, lorry 3.5-7.5 metric ton

transport, freight, lorry, 3.5t gross weight, unspecified powertrain

transport, freight, lorry, 26t gross weight, unspecified powertrain

transport, freight, lorry 7.5-16 metric ton

transport, freight, lorry, 7.5t gross weight, unspecified powertrain

transport, freight, lorry, 26t gross weight, unspecified powertrain

transport, freight, lorry >32 metric ton

transport, freight, lorry, 40t gross weight, unspecified powertrain

transport, freight, lorry, 40t gross weight, unspecified powertrain

transport, freight, lorry with reefer, cooling

transport, freight, lorry, unspecified

transport, freight, lorry, unspecified

transport, freight, lorry with reefer, freezing

transport, freight, lorry, unspecified

transport, freight, lorry, unspecified

transport, freight, lorry with refrigeration machine, 3.5-7.5 ton

transport, freight, lorry, 3.5t gross weight, unspecified powertrain

transport, freight, lorry, 26t gross weight, unspecified powertrain

transport, freight, lorry with refrigeration machine, 7.5-16 ton

transport, freight, lorry, 7.5t gross weight, unspecified powertrain

transport, freight, lorry, 26t gross weight, unspecified powertrain

transport, freight, lorry with refrigeration machine, cooling

transport, freight, lorry, unspecified

transport, freight, lorry, unspecified

transport, freight, lorry with refrigeration machine, freezing

transport, freight, lorry, unspecified

transport, freight, lorry, unspecified

Note that IMAGE fleet data only uses 26t and 40t trucks.

Additionally, premise iterates through each truck transport-consuming activities to calculate the driving distance required. When the reference unit of the dataset is 1 kilogram, the distance driven by truck can easily be inferred. Indeed, for example, 0.56 tkm of truck transport for 1 kg of flour indicates that the flour has been transported over 560 km.

On this basis, premise chooses one of the following driving cycles:

  • regional delivery, if the distance is inferior or equal to 450 km

  • long haul, if the distance is superior to 450 km

Hence, in the following dataset for “market for steel, low-alloyed” for the IAM region of India, premise chose the regional delivery driving cycle since the kilogram of steel has been transported on average over 120 km by truck. The truck used to transport that kilogram of steel is a fleet average vehicle built upon the REMIND fleet data for the region of India.

Output

_

_

_

producer

amount

unit

location

market for steel, low-alloyed

1

kilogram

IND

Input

supplier

amount

unit

location

market group for transport, freight, inland waterways, barge

0.5

ton kilometer

GLO

market group for transport, freight train

0.35

ton kilometer

GLO

market for transport, freight, sea, bulk carrier for dry goods

0.38

ton kilometer

GLO

transport, freight, lorry, unspecified, regional delivery

0.12

ton kilometer

IND

steel production, converter, low-alloyed

0.66

kilogram

IND

steel production, electric, low-alloyed

0.34

kilogram

IND

Direct Air Capture

Run

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
    scenarios=[
            {"model":"remind", "pathway":"SSP2-Base", "year":2028}
        ],
    source_db="ecoinvent 3.7 cutoff",
    source_version="3.7.1",
    key='xxxxxxxxxxxxxxxxxxxxxxxxx'
)
ndb.update("dac")

premise creates different region-specific Direct Air Capture (DAC) datasets, based on the inventories from Qiu et al., 2022.

If provided by the IAM scenario, premise scales the inputs of electricity and heat of the DAC datasets to reflect changes in efficiency.

Fuels

Run

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
    scenarios=[
            {"model":"remind", "pathway":"SSP2-Base", "year":2028}
        ],
    source_db="ecoinvent 3.7 cutoff",
    source_version="3.7.1",
    key='xxxxxxxxxxxxxxxxxxxxxxxxx'
)
ndb.update("fuels")

premise create different region-specific fuel supply chains and fuel markets, based on data from the IAM scenario.

The biomass-to-fuel efficiency ratio of bioethanol and biodiesel production datasets is adjusted according to the IAM scenario projections.

Inputs to the biofuel production datasets are multiplied by a scaling factor that represents the change in efficiency relative to today (2020).

Several pathways for hydrogen production are modeled in premise:

  • electrolysis

  • steam methane reforming of natural gas

  • steam methane reforming of biomethane

  • gasification of coal

  • gasification of woody biomass

The last four pathways are modeled with and without CCS.

Inventories for these pathways are available under:

  • premise/data/additional_inventories/lci-hydrogen-electrolysis.xlsx

  • premise/data/additional_inventories/lci-smr-atr-natgas.xlsx

  • premise/data/additional_inventories/lci-smr-atr-biogas.xlsx

  • premise/data/additional_inventories/lci-hydrogen-coal-gasification.xlsx

  • premise/data/additional_inventories/lci-hydrogen-wood-gasification.xlsx

In case the IAM variable that relates to a given hydrogen pathway’s efficiency is not available, the process’ efficiency is not modified, with the exception of electrolysis, which is modified regardless.

A scaling factor is calculated for each pathway, which is the ratio between the IAM variable value for the year in question and the current efficiency value (i.e., in 2020). premise uses this scaling factor to adjust the amount of feedstock input to produce 1 kg of hydrogen (e.g., m3 of natural gas per kg hydrogen).

If the IAM variable that relates to the efficiency of the electrolysis hydrogen process is not available, premise adjusts the amount of electricity needed to produce 1 kg of hydrogen by electrolysis, on the basis of the following requirements, which are sourced from Bauer et al, 2022:

kWh/kg H2, 25 bar

2010

2020

2050

electricity

58

55

44

When building a database using IMAGE, land use and land use change emissions are available. Upon the import of crops farming datasets, premise adjusts the land occupation as well as CO2 emissions associated to land use and land use change, respectively.

Output

_

_

_

producer

amount

unit

location

Farming and supply of corn

1

kilogram

CEU

Input

supplier

amount

unit

location

market for diesel, burned in agricultural machinery

0.142

megajoule

GLO

petrol, unleaded, burned in machinery

0.042

megajoule

GLO

market for natural gas, burned in gas motor, for storage

0.091

megajoule

GLO

market group for electricity, low voltage

0.004

kilowatt hour

CEU

Energy, gross calorific value, in biomass

15.910

megajoule

_

Occupation, annual crop

1.584

square meter-year

_

Carbon dioxide, in air

1.476

kilogram

_

Carbon dioxide, from soil or biomass stock

1.140

kilogram

_

The land use value is given from the IAM scenario in Ha/GJ of primary crop energy. Hence, the land occupation per kg of crop farmed is calculated as:

land_use = land_use [Ha/GJ] * 10000 [m2/Ha] / 1000 [MJ/GJ] * LHV [MJ/kg]

Regarding land use change CO2 emissions, the principle is similar. The variable is expressed in kg CO2/GJ of primary crop energy. Hence, the land use change CO2 emissions per kg of crop farmed are calculated as:

land_use_co2 = land_use_co2 [kg CO2/GJ] / 1000 [MJ/GJ] * LHV [MJ/kg]

premise builds several supply chains for synthetic fuels, for each IAM region. THe reason for this is that synthetic fuels can be produced from a variety of hydrogen and CO2 sources. Additionally, hydrogen can be supplied by different means of transport, and in different states.

premise starts by building different supply chains for hydrogen by varying:

  • the transport mode: truck, hydrogen pipeline, re-assigned CNG pipeline, ship,

  • the distance: 500 km, 2000 km

  • the state of the hydrogen: gaseous, liquid, liquid organic compound,

  • the hydrogen production route: electrolysis, SMR, biomass gasifier (coal, woody biomass)

Hence, for each IAM region, the following supply chains for hydrogen are built:

  • hydrogen supply, from electrolysis, by ship, as liquid, over 2000 km

  • hydrogen supply, from gasification of biomass by heatpipe reformer, by H2 pipeline, as gaseous, over 500 km

  • hydrogen supply, from ATR of from natural gas, by truck, as gaseous, over 500 km

  • hydrogen supply, from gasification of biomass by heatpipe reformer, by truck, as liquid organic compound, over 500 km

  • hydrogen supply, from SMR of from natural gas, with CCS, by truck, as liquid organic compound, over 500 km

  • hydrogen supply, from SMR of from natural gas, with CCS, by ship, as liquid, over 2000 km

  • hydrogen supply, from coal gasification, by CNG pipeline, as gaseous, over 500 km

  • hydrogen supply, from SMR of from natural gas, by ship, as liquid, over 2000 km

  • hydrogen supply, from coal gasification, by truck, as liquid, over 500 km

  • hydrogen supply, from gasification of biomass by heatpipe reformer, by truck, as liquid, over 500 km

  • hydrogen supply, from ATR of from natural gas, with CCS, by truck, as liquid organic compound, over 500 km

  • hydrogen supply, from SMR of from natural gas, with CCS, by truck, as liquid, over 500 km

  • hydrogen supply, from electrolysis, by truck, as liquid organic compound, over 500 km

  • hydrogen supply, from gasification of biomass, by truck, as liquid organic compound, over 500 km

  • hydrogen supply, from SMR of from natural gas, with CCS, by truck, as gaseous, over 500 km

  • hydrogen supply, from SMR of biogas, with CCS, by CNG pipeline, as gaseous, over 500 km

  • hydrogen supply, from SMR of from natural gas, by truck, as gaseous, over 500 km

  • hydrogen supply, from SMR of from natural gas, by H2 pipeline, as gaseous, over 500 km

  • hydrogen supply, from gasification of biomass, with CCS, by truck, as liquid organic compound, over 500 km

  • hydrogen supply, from gasification of biomass, by ship, as liquid, over 2000 km

Each supply route is associated with specific losses. Losses for the transport of H2 by truck and hydrogen pipelines, and losses at the regional storage storage (salt cavern) are from Wulf et al, 2018. Boil-off loss values during shipping are from Hank et al, 2020. Losses when transporting H2 via re-assigned CNG pipelines are from Cerniauskas et al, 2020. Losses along the pipeline are from Schori et al, 2012., but to be considered conservative, as those are initially for natural gas (and hydrogen has a higher potential for leaking).

_

_

truck

ship

H2 pipeline

CNG pipeline

reference flow

gaseous

compression

0.5%

0.5%

0.5%

per kg H2

_

storage buffer

2.3%

2.3%

per kg H2

_

storage leak

1.0%

1.0%

per kg H2

_

pipeline leak

0.004%

0.004%

per kg H2, per km

_

purification

7.0%

per kg H2

liquid

liquefaction

1.3%

1.3%

per kg H2

_

vaporization

2.0%

2.0%

per kg H2

_

boil-off

0.2%

0.2%

per kg H2, per day

liquid organic compound

hydrogenation

0.5%

per kg H2

Losses are cumulative along the supply chain and range anywhere between 5 and 20%. The table below shows the example of 1 kg of hydrogen transport via re-assigned CNG pipelines, as a gas, over 500 km. A total of 0.13 kg of hydrogen is lost along the supply chain (13% loss):

Output

_

_

_

producer

amount

unit

location

hydrogen supply, from electrolysis, by CNG pipeline, as gaseous, over 500 km

1

kilogram

OCE

Input

supplier

amount

unit

location

hydrogen production, gaseous, 25 bar, from electrolysis

1.133

kilogram

OCE

market group for electricity, low voltage

3.091

kilowatt hour

OCE

market group for electricity, low voltage

0.516

kilowatt hour

OCE

hydrogen embrittlement inhibition

1

kilogram

OCE

geological hydrogen storage

1

kilogram

OCE

Hydrogen refuelling station

1.14E-07

unit

OCE

distribution pipeline for hydrogen, reassigned CNG pipeline

1.56E-08

kilometer

RER

transmission pipeline for hydrogen, reassigned CNG pipeline

1.56E-08

kilometer

RER

  • 7% during the purification of hydrogen: when using CNG pipelines, the hydrogen has to be mixed with another gas to prevent the embrittlement of the pipelines. The separation process at the other end leads to significant losses

  • 2% lost along the 500 km of pipeline

  • 3% at the regional storage (salt cavern)

Also, in this same case, electricity is used:

  • 1.9 kWh to compress the H2 from 25 bar to 100 bar to inject it into the pipeline

  • 1.2 kWh to recompress the H2 along the pipeline every 250 km

  • 0.34 kWh for injecting and pumping H2 into a salt cavern

  • 2.46 kWh to blend the H2 with oxygen on one end, and purify on the other

  • 0.5 kWh to pre-cool the H2 at the fuelling station (necessary if used in fuel cells, for example)

premise builds markets for the following fuels:

  • market for petrol, unleaded

  • market for petrol, low-sulfur

  • market for diesel, low-sulfur

  • market for diesel

  • market for natural gas, high pressure

  • market for hydrogen, gaseous

based on the IAM scenario data regarding the composition of liquid and gaseous secondary energy carriers:

Warning

Some fuel types are not properly represented in the LCI database. Available inventories for biomass-based methanol production do not differentiate between wood and grass as the feedstock.

Note

Modelling choice: premise builds several potential supply chains for hydrogen. Because the logistics to supply hydrogen in the future is not known or indicated by the IAM, the choice is made to supply it by truck over 500 km, in a gaseous state.

Because not all competing fuels of a same type have similar calorific values, some adjustments are made. The table below shows the example of the market for gasoline, for the IMAGE region of Western Europe in 2050. The sum of fuel inputs is superior to 1 (i.e., 1.4 kg). This is because the market dataset as “1 kg” as reference unit, and methanol and bioethanol have low calorific values comparatively to petrol (i.e., 19.9 and 26.5 MJ/kg respectively, vs. 42.6 MJ/kg for gasoline). Hence, their inputs are scaled up to reach an average calorific value of 42.6 MJ/kg of fuel supplied by the market.

This is necessary as gasoline-consuming activities in the lCI database are modelled with the calorific value of conventional gasoline.

Output

_

_

_

producer

amount

unit

location

market for petrol, low-sulfur

1

kilogram

WEU

Input

supplier

amount

unit

location

petrol production, low-sulfur

0.550

kilogram

CH

market for methanol, from biomass

0.169

kilogram

CH

market for methanol, from biomass

0.148

kilogram

CH

market for methanol, from biomass

0.122

kilogram

CH

market for methanol, from biomass

0.122

kilogram

CH

Ethanol production, via fermentation, from switchgrass

0.060

kilogram

WEU

Ethanol production, via fermentation, from switchgrass, with CCS

0.053

kilogram

WEU

Ethanol production, via fermentation, from sugarbeet

0.051

kilogram

WEU

Ethanol production, via fermentation, from sugarbeet, with CCS

0.051

kilogram

WEU

Ethanol production, via fermentation, from poplar, with CCS

0.041

kilogram

WEU

Ethanol production, via fermentation, from poplar

0.041

kilogram

WEU

Run

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
    scenarios=[
            {"model":"remind", "pathway":"SSP2-Base", "year":2028}
        ],
    source_db="ecoinvent 3.7 cutoff",
    source_version="3.7.1",
    key='xxxxxxxxxxxxxxxxxxxxxxxxx'
)
ndb.update("heat")

Datasets that supply heat and steam via the combustion of natural gas and diesel are regionalized (made available for each region of the IAM model) and relinked to regional fuel markets. If the fuel market contains a share of non-fossil fuels, the CO2 emissions of the heat and steam production are split between fossil and non-fossil emissions. Once regionalized, the heat and steam production datasets relink to activities that require heat within the same region.

Here is a list of the heat and steam production datasets that are regionalized:

  • diesel, burned in …

  • steam production, as energy carrier, in chemical industry

  • heat production, natural gas, …

  • heat and power co-generation, natural gas, …

  • heat production, light fuel oil, …

  • heat production, softwood chips from forest, …

  • heat production, hardwood chips from forest, …

These datasets are relinked to the corresponding regionalized fuel market only if .update(“fuels”) has been run. Also, heat production datasets that use biomass as fuel input (e.g., softwood and hardwood chips) relink to the dataset market for biomass, used as fuel if update(“biomass”) has been run previously.

premise iterates through activities that consume any of the newly created fuel markets to update the way CO2 emissions are modelled. Based on the fuel market composition, CO2 emissions within the fuel-consuming activity are split between fossil and non-fossil emissions.

The table below shows the example where the CO2 emissions of a 3.5t truck have been split into biogenic and fossil fractions after re-link to the new diesel market of the REMIND region for India.

Output

before

after

_

_

producer

amount

amount

unit

location

transport, freight, lorry, diesel, 3.5t

1

1

ton-kilometer

IND

Input

supplier

amount

amount

unit

location

treatment of tyre wear emissions, lorry

-0.0009

-0.0009

kilogram

RER

market for road maintenance

0.0049

0.0049

meter-year

RER

market for road

0.0041

0.0041

meter-year

GLO

treatment of road wear emissions, lorry

-0.0008

-0.0008

kilogram

RER

market for refrigerant R134a

2.84E-05

2.84E-05

kilogram

GLO

treatment of brake wear emissions, lorry

-0.0005

-0.0005

kilogram

RER

Light duty truck, diesel, 3.5t

1.39E-05

1.39E-05

unit

RER

market for diesel, low-sulfur

0.1854

0.1854

kilogram

IND

Carbon dioxide, fossil

0.5840

0.5667

kilogram

_

Carbon dioxide, non-fossil

0.0000

0.0173

kilogram

_

Nitrogen oxides

0.0008

0.0008

kilogram

_

Nitrogen oxides

0.0003

0.0003

kilogram

_

Geographical mapping

IAM models have slightly different geographical resolutions and definitions.

Map of IMAGE regions

_images/map_image.png

Map of REMIND regions

_images/map_remind.png

premise uses the following correspondence between ecoinvent locations and IAM regions. This mapping is performed by the constructive_geometries implementation in the wurst library.

ecoinvent location

REMIND region

IMAGE region

AE

MEA

ME

AL

NEU

CEU

AM

REF

RUS

AO

SSA

RSAF

APAC

OAS

SEAS

AR

LAM

RSAM

AT

EUR

WEU

AU

CAZ

OCE

AZ

REF

RUS

BA

NEU

CEU

BD

OAS

RSAS

BE

EUR

WEU

BG

EUR

CEU

BH

MEA

ME

BJ

SSA

WAF

BN

OAS

SEAS

BO

LAM

RSAM

BR

LAM

BRA

BR-AC

LAM

BRA

BR-AL

LAM

BRA

BR-AM

LAM

BRA

BR-AP

LAM

BRA

BR-BA

LAM

BRA

BR-CE

LAM

BRA

BR-DF

LAM

BRA

BR-ES

LAM

BRA

BR-GO

LAM

BRA

BR-MA

LAM

BRA

BR-MG

LAM

BRA

BR-Mid-western grid

LAM

BRA

BR-MS

LAM

BRA

BR-MT

LAM

BRA

BR-North-eastern grid

LAM

BRA

BR-Northern grid

LAM

BRA

BR-PA

LAM

BRA

BR-PB

LAM

BRA

BR-PE

LAM

BRA

BR-PI

LAM

BRA

BR-PR

LAM

BRA

BR-RJ

LAM

BRA

BR-RN

LAM

BRA

BR-RO

LAM

BRA

BR-RR

LAM

BRA

BR-RS

LAM

BRA

BR-SC

LAM

BRA

BR-SE

LAM

BRA

BR-South-eastern grid

LAM

BRA

BR-Southern grid

LAM

BRA

BR-SP

LAM

BRA

BR-TO

LAM

BRA

BW

SSA

RSAF

BY

REF

UKR

CA

CAZ

CAN

CA-AB

CAZ

CAN

CA-BC

CAZ

CAN

CA-MB

CAZ

CAN

Canada without Quebec

CAZ

CAN

CA-NB

CAZ

CAN

CA-NF

CAZ

CAN

CA-NS

CAZ

CAN

CA-NT

CAZ

CAN

CA-NU

CAZ

CAN

CA-ON

CAZ

CAN

CA-PE

CAZ

CAN

CA-QC

CAZ

CAN

CA-SK

CAZ

CAN

CA-YK

CAZ

CAN

CD

SSA

WAF

CENTREL

EUR

CEU

CG

SSA

WAF

CH

NEU

WEU

CI

SSA

WAF

CL

LAM

RSAM

CM

SSA

WAF

CN

CHA

CHN

CN-AH

CHA

CHN

CN-BJ

CHA

CHN

CN-CQ

CHA

CHN

CN-CSG

CHA

CHN

CN-FJ

CHA

CHN

CN-GD

CHA

CHN

CN-GS

CHA

CHN

CN-GX

CHA

CHN

CN-GZ

CHA

CHN

CN-HA

CHA

CHN

CN-HB

CHA

CHN

CN-HE

CHA

CHN

CN-HL

CHA

CHN

CN-HN

CHA

CHN

CN-HU

CHA

CHN

CN-JL

CHA

CHN

CN-JS

CHA

CHN

CN-JX

CHA

CHN

CN-LN

CHA

CHN

CN-NM

CHA

CHN

CN-NX

CHA

CHN

CN-QH

CHA

CHN

CN-SA

CHA

CHN

CN-SC

CHA

CHN

CN-SD

CHA

CHN

CN-SGCC

CHA

CHN

CN-SH

CHA

CHN

CN-SX

CHA

CHN

CN-TJ

CHA

CHN

CN-XJ

CHA

CHN

CN-XZ

CHA

CHN

CN-YN

CHA

CHN

CN-ZJ

CHA

CHN

CO

LAM

RSAM

CR

LAM

RCAM

CU

LAM

RCAM

CW

LAM

RCAM

CY

EUR

CEU

CZ

EUR

CEU

DE

EUR

WEU

DK

EUR

WEU

DO

LAM

RCAM

DZ

MEA

NAF

EC

LAM

RSAM

EE

EUR

CEU

EG

MEA

NAF

ENTSO-E

EUR

WEU

ER

SSA

EAF

ES

EUR

WEU

ET

SSA

EAF

Europe without Austria

EUR

WEU

Europe without Switzerland

EUR

WEU

Europe without Switzerland and Austria

EUR

WEU

Europe, without Russia and Turkey

EUR

WEU

FI

EUR

WEU

FR

EUR

WEU

GA

SSA

WAF

GB

EUR

WEU

GE

REF

RUS

GH

SSA

WAF

GI

EUR

WEU

GLO

World

World

GR

EUR

WEU

GT

LAM

RCAM

HK

CHA

CHN

HN

LAM

RCAM

HR

EUR

CEU

HT

LAM

RCAM

HU

EUR

CEU

IAI Area, Africa

SSA

RSAF

IAI Area, Asia, without China and GCC

OAS

SEAS

IAI Area, EU27 & EFTA

EUR

WEU

IAI Area, Gulf Cooperation Council

MEA

ME

IAI Area, North America

USA

USA

IAI Area, Russia & RER w/o EU27 & EFTA

REF

RUS

IAI Area, South America

LAM

RSAM

ID

OAS

INDO

IE

EUR

WEU

IL

MEA

ME

IN

IND

INDIA

IN-AP

IND

INDIA

IN-AR

IND

INDIA

IN-AS

IND

INDIA

IN-BR

IND

INDIA

IN-CT

IND

INDIA

IN-DL

IND

INDIA

IN-Eastern grid

IND

INDIA

IN-GA

IND

INDIA

IN-GJ

IND

INDIA

IN-HP

IND

INDIA

IN-HR

IND

INDIA

IN-JH

IND

INDIA

IN-JK

IND

INDIA

IN-KA

IND

INDIA

IN-KL

IND

INDIA

IN-MH

IND

INDIA

IN-ML

IND

INDIA

IN-MN

IND

INDIA

IN-MP

IND

INDIA

IN-NL

IND

INDIA

IN-North-eastern grid

IND

INDIA

IN-Northern grid

IND

INDIA

IN-OR

IND

INDIA

IN-PB

IND

INDIA

IN-PY

IND

INDIA

IN-RJ

IND

INDIA

IN-SK

IND

INDIA

IN-Southern grid

IND

INDIA

IN-TN

IND

INDIA

IN-TR

IND

INDIA

IN-UP

IND

INDIA

IN-UT

IND

INDIA

IN-WB

IND

INDIA

IN-Western grid

IND

INDIA

IQ

MEA

ME

IR

MEA

ME

IS

NEU

WEU

IT

EUR

WEU

JM

LAM

RCAM

JO

MEA

ME

JP

JPN

JAP

KE

SSA

EAF

KG

REF

STAN

KH

OAS

SEAS

KP

OAS

KOR

KR

OAS

KOR

KW

MEA

ME

KZ

REF

STAN

LB

MEA

ME

LK

OAS

RSAS

LT

EUR

CEU

LU

EUR

WEU

LV

EUR

CEU

LY

MEA

NAF

MA

MEA

NAF

MD

REF

UKR

ME

NEU

ME

MG

SSA

EAF

MK

NEU

CEU

MM

OAS

SEAS

MN

OAS

CHN

MT

EUR

WEU

MU

SSA

EAF

MX

LAM

MEX

MY

OAS

SEAS

MZ

SSA

RSAF

NA

SSA

RSAF

NE

SSA

WAF

NG

SSA

WAF

NI

LAM

RCAM

NL

EUR

WEU

NO

NEU

WEU

NORDEL

NEU

WEU

North America without Quebec

USA

USA

NP

OAS

RSAS

NZ

CAZ

OCE

OCE

CAZ

OCE

OM

MEA

ME

PA

LAM

RCAM

PE

LAM

RSAM

PG

OAS

INDO

PH

OAS

SEAS

PK

OAS

RSAS

PL

EUR

CEU

PT

EUR

WEU

PY

LAM

RSAM

QA

MEA

ME

RAF

SSA

RSAF

RAS

CHA

CHN

RER

EUR

WEU

RER w/o CH+DE

EUR

WEU

RER w/o DE+NL+RU

EUR

WEU

RER w/o RU

EUR

WEU

RLA

LAM

RSAM

RME

MEA

ME

RNA

USA

USA

RO

EUR

CEU

RoW

World

World

RS

NEU

CEU

RU

REF

RUS

RW

SSA

EAF

SA

MEA

ME

SAS

IND

INDIA

SD

MEA

EAF

SE

EUR

WEU

SG

OAS

SEAS

SI

EUR

CEU

SK

EUR

CEU

SN

SSA

WAF

SS

SSA

EAF

SV

LAM

RCAM

SY

MEA

ME

TG

SSA

WAF

TH

OAS

SEAS

TJ

REF

STAN

TM

REF

STAN

TN

MEA

NAF

TR

MEA

TUR

TT

LAM

RCAM

TW

CHA

CHN

TZ

SSA

RSAF

UA

REF

UKR

UCTE

EUR

WEU

UCTE without Germany

EUR

WEU

UN-OCEANIA

CAZ

OCE

UN-SEASIA

OAS

SEAS

US

USA

USA

US-ASCC

USA

USA

US-HICC

USA

USA

US-MRO

USA

USA

US-NPCC

USA

USA

US-PR

USA

USA

US-RFC

USA

USA

US-SERC

USA

USA

US-TRE

USA

USA

US-WECC

USA

USA

UY

LAM

RSAM

UZ

REF

STAN

VE

LAM

RSAM

VN

OAS

SEAS

WECC

USA

USA

WEU

EUR

WEU

XK

EUR

CEU

YE

MEA

ME

ZA

SSA

SAF

ZM

SSA

RSAF

ZW

SSA

RSAF

Regionalization

Several of the integration steps described above involve the regionalization of datasets. It is the case, for example, when introducing datasets representing a process for each of the IAM regions. In such case, the datasets are regionalized by selecting the most representative suppliers of inputs for each region. If a dataset in a specific IAM region requires tap water, for example, the regionalization process will select the most representative water suppliers in that region.

If more than one supplier is available, the regionalization process will allocated a supply share to each candidate supplier based on their respective production volume. If no adequate supplier is found for a given region, the regionalization process will select all the existing suppliers and allocate a supply share to each supplier based on their respective production volume.

Here is the decision tree followed:

Decision Tree for Processing Datasets

The process begins with a dataset that requires processing.

Decision: Is the Exchange in Cache?

  • Yes

    • Use process_cached_exchange().

      • Retrieve cached data.

      • Update new_exchanges with cached data.

  • No

    • Use process_uncached_exchange().

      • None

        • Print a warning and return.

      • One

        • Use handle_single_possible_dataset().

          • Use the single matched dataset.

          • Update new_exchanges with this dataset information.

      • Multiple

        • Use handle_multiple_possible_datasets().

          • Yes

            • Use the matched dataset location.

          • No

            • Use process_complex_matching_and_allocation().

              • IAM Region

                • Use handle_iam_region().

                  • Match IAM region to ecoinvent locations.

                  • Update new_exchanges with IAM region-specific data.

                  • Cache the new entry.

              • Global (‘GLO’, ‘RoW’, ‘World’)

                • Use handle_global_and_row_scenarios().

                  • Allocate inputs for global datasets.

                  • Update new_exchanges with global data.

                  • Cache the new entry.

              • Others

                • Perform GIS matching.

                  • Determine intersecting locations with GIS.

                  • Allocate inputs based on GIS matches.

                  • Update new_exchanges with GIS-specific data.

                  • Cache the new entry.

Final Steps

  • If no match is found, use handle_default_option().

    • Integrate new exchanges into the dataset.

GAINS emission factors

Run

from premise import *
import brightway2 as bw

bw.projects.set_current("my_project)

ndb = NewDatabase(
    scenarios=[
            {"model":"remind", "pathway":"SSP2-Base", "year":2028}
        ],
    source_db="ecoinvent 3.7 cutoff",
    source_version="3.7.1",
    key='xxxxxxxxxxxxxxxxxxxxxxxxx'
)
ndb.update("emissions")

When using update(“emissions”), emission factors from the GAINS-EU and GAINS-IAM models are used to scale non-CO2 emissions in various datasets.

The emission factors are available under https://github.com/polca/premise/tree/master/premise/data/GAINS_emission_factors

Emission factors from GAINS-EU are applied to activities in European countries. Emission factors from GAINS-IAM are applied to activities in non-European countries, or to European activities if an emission facor from GAINS-EU has not been applied first.

Emission factors are specific to:

  • an activity type,

  • a year,

  • a country (for GAINS-EU, otherwise a region),

  • a fuel type,

  • a technology type,

  • and a scenario.

The mapping between GAINS and ecoinvent activities is available under the following file: https://github.com/polca/premise/blob/master/premise/data/GAINS_emission_factors/gains_ecoinvent_sectoral_mapping.yaml

The table below shows the mapping between ecoinvent and GAINS emission flows.

ecoinvent species

GAINS species

Sulfur dioxide

SO2

Sulfur oxides

SO2

Carbon monoxide, fossil

CO

Carbon monoxide, non-fossil

CO

Carbon monoxide, from soil or biomass stock

CO

Nitrogen oxides

NOx

Ammonia

NH3

NMVOC, non-methane volatile organic compounds, unspecified origin

VOC

VOC, volatile organic compounds, unspecified origin

VOC

Methane

CH4

Methane, fossil

CH4

Methane, non-fossil

CH4

Methane, from soil or biomass stock

CH4

Dinitrogen monoxide

N2O

Particulates, > 10 um

PM10

Particulates, > 2.5 um, and < 10um

PM25

Particulates, < 2.5 um

PM1

We consider emission factors in ecoinvent as representative of the current situation. Hence, we calculate a scaling factor from the GAINS emission factors for the year of the scenario relative to the year 2020. note that premise prevents scaling factors to be inferior to 1 if the year is inferior to 2020. Inversely, scaling factors cannot be superior to 1 if the year is superior to 2020.

Two GAINS-IAM scenarios are available:

  • CLE: **C**urrent **LE**gislation scenario

  • MFR: **M**aximum **F**easible **R**eduction scenario

By default, the CLE scenario is used. To use the MFR scenario:

ndb = NewDatabase(
    ...
    gains_scenario="MFR",
)

Finally, unlike GAINS-EU, GAINS-IAM uses IAM-like regions, not countries. The mapping between IAM regions and GAINS-IAM regions is available under the following file:

https://github.com/polca/premise/blob/master/premise/iam_variables_mapping/gains_regions_mapping.yaml

For questions related to GAINS modelling, please contact the respective GAINS team:

Logs

premise generates a spreadsheet report detailing changes made to the database for each scenario. The report is saved in the current working directory and is automatically generated after database export.

The report lists the datasets added, updated and emptied. It also gives a number of indicators relating to efficiency, emissions, etc. for each scenario.

Finally, it also contains a “Validation” tab that lists datasets which potentially present erroneous values. These datasets are to be checked by the user.

This report can also be generated manually using the generate_change_report() method.

LOAD

Back to a brightway2 project

Regular brightway2 database

premise uses bw2io to load the LCI database back into a brightway2 project. This is done as follows:

ndb.write_db_to_brightway()

If several databases have been built, the user can give them specific names, like so:

ndb.write_db_to_brightway(name=["db_1", "db_2"])

Superstructure database

If several scenario databases are built, premise can generate a superstructure database, as explained in Steubing et al, 2021. This allows to explore several scenarios while writing only one database in a brightway2 project. Besides writing the database to disk, this also creates a scenario difference file that will be read by Activity-Browser.

This is done as follows:

ndb.write_superstructure_db_to_brightway()

You can also specify a file path for the export of the scenario difference file:

ndb.write_superstructure_db_to_brightway(filepath="some_file_path")

Finally, you can also give a name to the superstructure database:

ndb.write_superstructure_db_to_brightway(filepath="some_file_path", name="my_db")

Note

Superstructure databases can only be used by Activity-Browser at the moment.

As sparse matrices

premise can generate a sparse matrix representation of the database(s). This is useful when no LCA software can be used, or when connections to SQL databases should be avoided.

This is done as follows:

ndb.write_db_to_matrices()

This creates a set of CSV files:

  • a CSV file that represents product exchanges between activities, under the form [a, b, x]

  • a CSV file that represent natural flow exchanges between activities and the biosphere, under the form [a, c, x]

  • and another two CSV files contains the mapping between the activity names are the indices in the matrices

with a being the row index of an activity, b being the column index of an activity, c being a natural flow, and x being the value exchanged.

For example, the following piece of script calculates the GWP score of all activities in the database:

""" COLLECT DATA """
# creates dict of activities <--> indices in A matrix
A_inds = dict()
with open("A_matrix_index.csv", 'r') as read_obj:
    csv_reader = reader(read_obj, delimiter=";")
    for row in csv_reader:
        A_inds[(row[0], row[1], row[2], row[3])] = row[4]
A_inds_rev = {int(v):k for k, v in A_inds.items()}

# creates dict of bio flow <--> indices in B matrix
B_inds = dict()
with open("B_matrix_index.csv", 'r') as read_obj:
    csv_reader = reader(read_obj, delimiter=";")
    for row in csv_reader:
        B_inds[(row[0], row[1], row[2], row[3])] = row[4]
B_inds_rev = {int(v):k for k, v in B_inds.items()}

# create a sparse A matrix
A_coords = np.genfromtxt("A_matrix.csv", delimiter=";", skip_header=1)
I = A_coords[:, 0].astype(int)
J = A_coords[:, 1].astype(int)
A = sparse.csr_matrix((A_coords[:,2], (J, I)))

# create a sparse B matrix
B_coords = np.genfromtxt("B_matrix.csv", delimiter=";", skip_header=1)
I = B_coords[:, 0].astype(int)
J = B_coords[:, 1].astype(int)
B = sparse.csr_matrix((B_coords[:,2] *- 1, (I, J)), shape=(A.shape[0], len(B_inds)))

# a vector with a few GWP CFs
gwp = np.zeros(B.shape[1])

gwp[[int(B_inds[x]) for x in B_inds if x[0]=="Carbon dioxide, non-fossil, resource correction"]] = -1
gwp[[int(B_inds[x]) for x in B_inds if x[0]=="Hydrogen"]] = 5
gwp[[int(B_inds[x]) for x in B_inds if x[0]=="Carbon dioxide, in air"]] = -1
gwp[[int(B_inds[x]) for x in B_inds if x[0]=="Carbon dioxide, non-fossil"]] = 1
gwp[[int(B_inds[x]) for x in B_inds if x[0]=="Carbon dioxide, fossil"]] = 1
gwp[[int(B_inds[x]) for x in B_inds if x[0]=="Carbon dioxide, from soil or biomass stock"]] = 1
gwp[[int(B_inds[x]) for x in B_inds if x[0]=="Carbon dioxide, to soil or biomass stock"]] = -1

l_res = []
for v in range(0, A.shape[0]):
    f = np.float64(np.zeros(A.shape[0]))
    f[v] = 1
    A_inv = spsolve(A, f)
    C = A_inv * B
    l_res.append((C * gwp).sum())

As Simapro CSV files

premise can export the databases as Simapro-CSV files.

This is done as follows:

ndb.write_db_to_simapro()

Note

The categorization of activities in the Simapro activity tree looks different from that of the original ecoinvent database accessed from Simapro. That is because premise relies on ISIC v.4 and CCP classifications to categorize activities. Also, a number of activities do not have a category and are found under Meterials/Others.

As Simapro CSV files for OpenLCA

premise can export the databases as a modified version of Simapro-CSV files compatible with OpenLCA.

This is done as follows:

ndb.write_db_to_olca()

Note

The categorization of imported activities may differ from OpenLCA’s original classification.

The Simapro CSV files can be imported in OpenLCA in a new database like so:

_images/olca_fig1.png

You will need to select “SimaproCSV_Import.csv” as mapping file to use.

_images/olca_fig2.png

Finally, once imported, unlinked flows remain. They can be found under these highlighted folders:

_images/olca_fig3.png

To link them, you need to import an additional mapping flow that you can find here (“Tools” > “Flow mapping” > “Open file”).

_images/olca_fig4.png

And then go to “Flow mapping” > “Apply on database”. A few dozens of unlinked flows will remain. You may fix that by manually mapping them.

As a data package

premise can export the databases as a data package, which is a standardized way of packaging data. This is useful when you want to share your databases with others, without sharing the source database (i.e., ecoinvent), which is under restrictive license.

This is done as follows:

ndb.write_db_to_datapackage()

This creates a zip file that contains the all the data necessary for other users to replicate the databases, provided they have access to the source database locally.

See the library <unfold https://github.com/polca/unfold/tree/main>_ for more information on data packages for sharing LCA databases. unfold can read these data packages and create brightway2 databases (or superstructure databases) from them. unfold can also fold premise databases registered in your brightway2 project into data packages, to be shared with and recreated by others.

Mapping

IAM scenario file

The scenario file should be a comma-separated text file (i.e., csv) with data presented in a tabular format, such as:

Model

Scenario

Region

Variable

Unit

2005

2010

2015

2020

2025

REMIND

SSP2EU-Base

CAZ

Emi|CO2|+|Energy

Mt CO2/yr

1011.34074

976.7202877

993.8525168

957.3199102

945.014101

REMIND

SSP2EU-Base

CHA

Emi|CO2|+|Energy

Mt CO2/yr

6720.313463

8601.575671

10086.37126

11281.46999

10996.79931

REMIND

SSP2EU-Base

EUR

Emi|CO2|+|Energy

Mt CO2/yr

4235.648974

3730.532814

3392.421123

3114.284044

2860.549231

REMIND

SSP2EU-Base

IND

Emi|CO2|+|Energy

Mt CO2/yr

1215.466496

1664.185158

2146.940653

2477.459967

2946.357462

REMIND

SSP2EU-Base

JPN

Emi|CO2|+|Energy

Mt CO2/yr

1457.252288

1415.666384

1345.278014

1181.679212

1060.684659

REMIND

SSP2EU-Base

LAM

Emi|CO2|+|Energy

Mt CO2/yr

1410.609298

1575.558465

1682.930038

1613.4512

1739.260156

REMIND

SSP2EU-Base

MEA

Emi|CO2|+|Energy

Mt CO2/yr

1782.408233

2254.050107

2607.952516

2793.972343

3064.426497

REMIND

SSP2EU-Base

NEU

Emi|CO2|+|Energy

Mt CO2/yr

378.1710003

421.2277231

477.6241091

498.465216

500.4845903

REMIND

SSP2EU-Base

OAS

Emi|CO2|+|Energy

Mt CO2/yr

1787.07182

2073.863804

2442.52372

2780.880819

3264.746917

REMIND

SSP2EU-Base

REF

Emi|CO2|+|Energy

Mt CO2/yr

2551.110779

2472.637216

2544.690495

2607.286302

2681.647657

The following columns must be present:

  • Region

  • Variable

  • Unit

as well as the time steps (e..g, 2005 to 2100). Other columns can be present, but they will be ignored.

You need to point to that file when initiating NewDatabase, like so:

ndb = NewDatabase(
    scenarios = [{"model":"remind", "pathway":"my_special_scenario", "year":2028,
                  "filepath":r"C:\filepath\to\your\scenario\folder"}],
    source_db="ecoinvent 3.6 cutoff", # <-- name of the database
    source_version="3.6", # <-- version of ecoinvent
)

There are essentially two types of variables needed from the IAM scenario files:

  • variables that relate to the production volumes of technologies. These variables are used to scale the production volumes of the corresponding activities in the ecoinvent database. For example, if the IAM scenario file contains a variable named Electricity|Production|Wind for the region EUR, it will help premise calculate the share of wind power in the electricity consumption mix of the said region. Hence, the unit of such variables should refer to a production volume over time (e.g., GWh/year, EJ/year, etc.).

  • variables that relate to the efficiency of technologies over time. These variables are used to calculate scaling factors (which are relative by default to 2020), to adjust the energy or material efficiency of the corresponding activities in the ecoinvent database. For example, if the IAM scenario file contains a variable named Electricity|Efficiency|Coal for the region EUR, it will help premise adjust the amount of coal and related emissions per unit of kWh produced in the said region. Hence, the unit of such variables can be unitless, or relate to an efficiency ratio or percentage.

User-defined scenarios

Purpose

premise enables users to seamlessly integrate custom scenarios, in addition to (or as an alternative to) existing IAM scenarios. This feature is particularly useful when users wish to incorporate projections for a sector, product, or technology that may not be adequately addressed by standard IAM scenarios.

Available user-defined scenarios

Link to public repository of user-defined scenarios:

https://github.com/premise-community-scenarios

Using user-generated scenarios

To put it simply, users must first obtain the URL of the datapackage.json file corresponding to the desired scenario. By utilizing the datapackage library, users can load the scenario package, which includes a scenario file, inventories, and a configuration file. This package can then be added as an argument to the premise instance. Users have the flexibility to include any number of custom scenarios in this list. However, compatibility between user-defined scenarios is not guaranteed.

Example

from premise import *
import brightway2 as bw
from datapackage import Package
bw.projects.set_current("ei_38")

fp = r"https://raw.githubusercontent.com/premise-community-scenarios/cobalt-perspective-2050/main/datapackage.json"
cobalt = Package(fp)

ndb = NewDatabase(
scenarios = [
    {"model":"image", "pathway":"SSP2-Base", "year":2025},
    {"model":"image", "pathway":"SSP2-Base", "year":2030},
],
source_db="ecoinvent cutoff 3.8",
source_version="3.8",
key='xxxxxxx',
external_scenarios=[
    cobalt,
]

The function ndb.update(“external”) can be called after that to implement the user-defined scenario in the database.

ndb.update("external")

Of course, if you wish your database to also integrate the projections of the global IAM model, you can run the function ndb.update().

ndb.update()

Or if you just want the IAM projections relating to, for example, electricity and steel:

ndb.update([
    "electricity",
    "steel",
    "external"
])

Once the integrations are complete, you can export your databases to Brightway2, within the activated project:

ndb.write_db_to_brightway(name="my_custom_db_2025", "my_custom_db_2030")

Or as a SuperStructure database, which allows you to export only one database to Brightway2, regardless of the number of scenarios:

ndb.write_superstructure_db_to_brightway()

Note

SuperStructure databases can only be used from the Activity-Browser.

You can also export the databases to a csv file, which can be used by Simapro, or as a set of sparse matrices.

Producing your own scenario

The user can produce his/her own scenario by following the steps below:

  1. Clone an existing scenario repository from the public repository.

  2. Modify the scenario file (scenario_data/scenario_data.csv).

  3. Add any inventories needed, under inventories/lci-xxx.csv.

  4. Modify the configuration file (configuration_file/config.yaml), to instruct premise what to do.

  5. Ensure that the file names and paths above are consistent with what is indicated in datapackage.json.

  6. Once definitive, you can contact the admin of the public repository to add your scenario to the repository.

Example with Ammonia scenarios

Using ammonia as an example, this guide demonstrates how to create prospective databases from custom scenarios and other background scenarios using premise.

First, clone the Ammonia scenario repository:

git clone https://github.com/premise-community-scenarios/ammonia-prospective-scenarios.git

This command downloads a copy of the repository to your local machine. You can then rename and modify it as desired.

A datapackage requires four files (referred to as resources) to define a scenario:

  1. datapackage.json: A datapackage descriptor file that specifies the scenario author, name, description, version, and the file names and paths of the scenario file, configuration file, and inventories.

  2. scenario_data.csv: A scenario file that outlines various variables (e.g., production volumes, efficiencies) across time, space, and scenarios.

  3. config.yaml: A configuration file that instructs premise on the required actions. It provides information on the technologies considered in the scenario, their names in the scenario data file and inventories, and the inventories to use for each technology. Additionally, it indicates the markets to be created and their corresponding regions.

  4. lci-xxx.csv: Optional; a CSV file containing the inventories of the scenario, which is necessary if the LCA database lacks the required inventories.

datapackage.json

The datapackage.json file is a descriptor file that indicates the scenario author, scenario name, scenario description, scenario version, and the file names and paths of the scenario file, configuration file, and inventories.

Example:

{
    "profile": "data-package",
    "name": "ammonia-prospective-scenarios",
    "title": "Ammonia decarbonisation pathways and their effects on life cycle assessments: Integrating future ammonia scenarios into background data for prospective LCAs",
    "description": "Implementation of the scenarios on future ammonia supply from the Master thesis of J. Boyce, 2022.",
    "source":"Boyce, J. C. (2022). Ammonia decarbonisation pathways and their effects on life cycle assessments: Integrating future ammonia scenarios into background data for prospective LCAs [Master’s Thesis, Leiden University and TU Delft].",
    "version": "0.0.1",
    "contributors":[
        {
        "title": "Johanna C. Boyce",
        "email": "xxxx@umail.leidenuniv.nl"
}

The mapping between IAM scenarios and user-defined scenarios is established within the datapackage.json file. For instance, the SSP2-Base scenario from IAM models IMAGE and REMIND is mapped to the user-defined scenario Business As Usual. This implies that when users opt for the SSP2-Base scenario from IMAGE and REMIND, the user-defined scenario Business As Usual will be selected. Although your custom scenario may not be intended for use alongside an IAM scenario, it must still be mapped to one (this aspect could be improved in the future).

"scenarios": {
    "Business As Usual": [
        {
            "model": "image",
            "pathway": "SSP2-Base"
        },
        {
            "model": "remind",
            "pathway": "SSP2-Base"
        }
    ],

The resources section of the datapackage.json file indicates the file names, location of the scenario file, configuration file, and inventories, as well as how their data should present.

For example, here the scenario file is called scenario_data.csv, and is located in the scenario_data folder. The data in the file is in the long format, with the columns region, year, scenario, variable, etc. A scenario is, along with a configuration file, a mandatory resource of a scenario package – inventories are optional.

"resources": [
    {
        "path": "scenario_data/scenario_data.csv",
        "profile": "tabular-data-resource",
        "name": "scenario_data",
        "format": "csv",
        "mediatype": "text/csv",
        "encoding": "utf-8-sig",
        "schema": {
            "fields": [
                {
                    "name": "model",
                    "type": "string",
                    "format": "default"
                },

Scenario data

The scenario_data.csv file contains the scenario data. Having this file as a csv is mandatory, as it allows to track changes between scenario versions. Below are shown some variables that indicate the efficiency of the production of hydrogen from alkaline-based electrolysers, from 2020 to 2050, for the Sustainable development scenario, for several regions. The actual meaning of this variable is not important here, as it is defined in the configuration file.

model

pathway

scenario

region

variables

unit

2020

2025

2030

2035

2040

2045

2050

2100

image

SSP2-RCP19

Sustainable development

CHN

Efficiency|Hydrogen|Alkaline Electrolysis (electricity)

%

66

67.5

69

71

73

74.5

76

76

image

SSP2-RCP19

Sustainable development

INDIA

Efficiency|Hydrogen|Alkaline Electrolysis (electricity)

%

66

67.5

69

71

73

74.5

76

76

image

SSP2-RCP19

Sustainable development

CAN

Efficiency|Hydrogen|Alkaline Electrolysis (electricity)

%

66

67.5

69

71

73

74.5

76

76

image

SSP2-RCP19

Sustainable development

USA

Efficiency|Hydrogen|Alkaline Electrolysis (electricity)

%

66

67.5

69

71

73

74.5

76

76

image

SSP2-RCP19

Sustainable development

MEX

Efficiency|Hydrogen|Alkaline Electrolysis (electricity)

%

66

67.5

69

71

73

74.5

76

76

The first column is the model column, which indicates the IAM model that the scenario maps with. The second column is the pathway column, which indicates the IAM scenario that the user-defined scenario should map with. The third column is the name of the user-defined scenario. The fourth column is the region, which can be either a country or a region. The fifth column is the variable column, which indicates the variable that the scenario data is about. The sixth column is the unit column, which indicates the unit of that variable. The columns after that are the values of the variable across time.

Variables can be production volumes (used to build markets), efficiencies, or other variables that are needed to modify/adjust inventories.

Inventories

Inventories are stored in csv files (for version control). The name of the csv file should be similar to what is indicated in the datapackage.json file. For example, if the datapackage.json file indicates that the inventory file is inventories/lci-xxx.csv, then the inventory file should be named lci-xxx.csv under the folder inventories in the root folder.

config.yaml

The config.yaml file is a configuration file that indicates the mapping between the variables in the scenario data and the variables in the LCA inventories.

It is composed of two main parts: production pathways and markets. The production pathways part indicates the mapping between the variables representing a production route and listed in the scenario data file, with the names of the LCI datasets. It is where one can indicate the efficiency of a production route, the amount of electricity used, the amount of hydrogen used, etc.

Consider the following example:

# `production pathways` lists the different technologies
production pathways:
  # name given to a technology: this name is internal to premise
  MP:
    # variables to look for in the scenario data file to fetch production volumes
    # values fetched from the scenario data file as production volumes are used to calculate
    # the supply share if markets are to be built
    production volume:
      # `variable` in `production volume` refers to the variable name in the scenario data file
      variable: Production|Ammonia|Methane Pyrolysis
    # dataset in the imported inventories that represents the technology
    ecoinvent alias:
      # name of the original dataset
      name: ammonia production, hydrogen from methane pyrolysis
      # reference product of the original dataset
      reference product: ammonia, anhydrous, liquid
      # indicate some string that should not be contained in the dataset name
      mask: solid
      # indicate whether the dataset exists in the original database
      # or if it should be sourced from the inventories folder
      exists in original database: False
      # indicate whether a region-specific version of the dataset should be created
      regionalize: True
      # indicate if the production volume from the scenario data should be multiplied by a factor
      # to account, for exmaple, for a difference in units relative to the other inputs (e.g., here, cubic meter instead of kilogram)
      ratio: 0.78

This excerpt from the config.yaml file indicates that the variable Production|Ammonia|Methane Pyrolysis in the scenario data file should be mapped with the dataset ammonia production, hydrogen from methane pyrolysis in the LCA inventories. The reference product of the dataset is ammonia, anhydrous, liquid. The regionalize parameter indicates that a region-specific version of the dataset should be created for each region listed in the scenario data file in the region column. The exists in original database parameter indicates that the dataset does not exist in the original database, but is sourced from the inventories folder.

Also, consider this other example from the config.yaml file:

#adding PEM and AE separately to make a sub-market
# and allow for efficiency improvements to the
# electrolysis processes
AE:
  production volume:
    variable: Production|Hydrogen|Alkaline Electrolysis
  ecoinvent alias:
    name: hydrogen production, alkaline electrolysis
    reference product: hydrogen, alkaline electrolysis
    exists in original database: False
    regionalize: True
  efficiency:
    - variable: Efficiency|Hydrogen|Alkaline Electrolysis (electricity)
      reference year: 2020
      includes:
        # efficiency gains will only apply to technosphere flows whose name
        # contains `electricity`
        technosphere:
          - electricity
      excludes:
          # but not to flows whose name contains `renewable` and `hydro`
          technosphere:
              - renewable
              - hydro

This is essentially the same as above, but it indicates that the variable Efficiency|Hydrogen|Alkaline Electrolysis (electricity) in the scenario data file should be mapped with the efficiency of the dataset hydrogen production, alkaline electrolysis in the LCA inventories.

The includes parameter indicates that the efficiency gains will only apply to flows of type technosphere whose name contains electricity. In practice, this will reduce the input of electricity over time for that dataset. If you do not specify includes, then the efficiency gains will apply to all flows (of type technosphere and biosphere).

The field reference year indicates the baseline year premise should use to calculate the factor by which the flows should be scaled by. For example, if the electrolyzer has an efficiency of 60% in 2020, and 70% in 2030, the input of electricity will be reduced by 14.3% (1 / (70%/60%)) if the database is created for 2030.

The markets part indicates which markets to build, which production routes these markets should be composed of, which inputs should they provide, and if they substitute a prior market in the database.

Consider the following example from the config.yaml file:

# name of the market dataset
- name: market for ammonia (APS)
  reference product: ammonia, anhydrous, liquid
  # unit of the market dataset
  unit: kilogram
  # names of datasets that should compose the market
  includes:
    - MP
    - SMR
    - SMR_w_CCS
    - ELE
    - OIL
    - CG
    - CGC
  # 'market for ammonia` will replace the existing markets.
  replaces:
    - name: market for ammonia, anhydrous, liquid
      reference product: ammonia, anhydrous, liquid
  # but only in German datasets
  replaces in:
    - location: DE

  # indicates that the market is a fuel market and emissions of activities
  # using this market as a supplier should be adjusted
  is fuel:
    petrol:
      Carbon dioxide, fossil: 3.15
      Carbon dioxide, non-fossil: 0.0
    bioethanol:
      Carbon dioxide, fossil: 0.0
      Carbon dioxide, non-fossil: 3.15

  # we also want to manually add some emissions to the market
  add:
    - name: market for electricity, low voltage
      reference product: electricity, low voltage
      amount: 0.0067

  # If true, flip signs
  waste market: False

This tells premise to build a market dataset named market for ammonia (APS) with the reference product ammonia, anhydrous, liquid and the unit kilogram. The market should be composed of the production routes MP, SMR, SMR_w_CCS, ELE, OIL, CG, and CGC, which have been defined in the production pathways part of the config.yaml file. The market will replace the existing market dataset market for ammonia, anhydrous, liquid.

The replaces parameter is optional. If it is not provided, the market will be added to the database without replacing any existing supplier.

The replaces in parameter is also optional. If it is not provided, the market will be replaced in all regions. In this case, the market will only be replaced in the regions indicated in the replaces in parameter. But replaces in is flexible. For example, instead of a region, you can indicate a string that should be contain in the name or reference product of activities to update.

The is fuel parameter is optional. It indicates that the market is a fuel market. The petrol and bioethanol parameters indicate the emissions associated with the production of petrol and bioethanol, respectively. The emissions are in kg CO2 per kg of fuel. Indicating this will adjust the indicated flows in any activity that uses the market as a supplier.

# name of the market dataset
- name: market for ammonia (APS)
  reference product: ammonia, anhydrous, liquid
  # unit of the market dataset
  unit: kilogram
  # names of datasets that should compose the market
  includes:
    - MP
    - SMR
    - SMR_w_CCS
    - ELE
    - OIL
    - CG
    - CGC
  # 'market for ammonia` will replace the existing markets.
  replaces:
    - name: market for ammonia, anhydrous, liquid
      reference product: ammonia, anhydrous, liquid
  replaces in:
    - reference product: urea
    - location: DE

Hence, in this example, the ammonia supplier will be replaced in all activities whose reference product contains the string urea and location in DE.

Main contributors

Consequential modelling

The premise module allows users to import and adjust the consequential system model of the ecoinvent database v3.8 and 3.9, with a focus on electricity and fuel markets. This work is based on a publication with available at https://doi.org/10.1016/j.rser.2023.113830

If you use this module, please cite the publication:

Ben Maes, Romain Sacchi, Bernhard Steubing, Massimo Pizzol, Amaryllis Audenaert, Bart Craeye, Matthias Buyle, Prospective consequential life cycle assessment: Identifying the future marginal suppliers using integrated assessment models, Renewable and Sustainable Energy Reviews, Volume 188, 2023, doi: 10.1016/j.rser.2023.113830

Currently, the identification of marginal supplying technologies is limited to the electricity and fuel sectors.

Some technologies are excluded from the marginal markets due to constraints on their feedstock availability. This typically applies to waste-to-energy (e.g., waste-based CHP) or waste-to-fuel (e.g., residue-based biofuel) plants. For steel markets, only the BF-BOF route is considered.

Some imported inventories cannot be directly linked to the ecoinvent consequential database. To address this, a mapping file is provided under https://github.com/polca/premise/blob/master/premise/data/consequential/blacklist.yaml which proposes alternative candidates to link to the ecoinvent consequential database.

How does it work?

From the user viewpoint, the process is as follows:

  • prepare a set of parameters that condition the identification of the marginal electricity suppliers

  • supply the parameters to NewDatabase()

  • point to the your local ecoinvent consequential database

The parameters used to identify marginal suppliers that make up a market are:

  • range time (years, default = 2)

  • duration (years, default = 0)

  • foresight (True or False, default = False)

  • lead time (True or False, default = False)

  • capital replacement rate (True or False, default = False)

  • measurement (0 to 4, default = 0)

  • weighted slope start (default = 0.75)

  • weighted slope end (default = 1.00)

_images/Time_interval.png

Techniques to determine the time interval of a study considering the supplier’s foresight and the duration of the change.

Range time

Integer. Years. Used for single occurrences or short-lasting changes in demand (less than 3 years). Since the duration of the change is too short to measure a trend, the trend is instead measured around the point where the additional capital will be installed. A range of n years before and after the point is taken as the time interval. Note that if set to a value other than 0, the duration argument must be set to 0. A default range of 2 years is chosen. This value closely mirrors the recommended time interval in ecoinvent’s consequential database, which is 3-4 years.

Duration

Integer. Years. Used for long-lasting changes in demand (3 years or more). Duration over which the change in demand occurs should be measured. Note that if set to a value other than 0, the range time argument must be set to 0.

Foresight

True or False. In the myopic approach (False), also called a recursive dynamic approach, the agents have no foresight on relevant parameters (e.g., energy demand, policy changes and prices) and will only act based on the information they can observe. In this case, the suppliers can answer to a change in demand only after it has occurred. In the perfect foresight approach, the future (within the studied time period) is fully known to all agents. In this case, the decision to invest can be made ahead of the change in demand. For suppliers with no foresight, capital will show up a lead time later.

Lead time

True or False. If False, the market average lead time is taken for all technologies. If True, technology-specific lead times are used. If Range and Duration are both set to False, then the lead time is taken as the time interval (just as with ecoinvent v.3.4).

If you wish to modify the default lead time values used for the different technologies, you can do so by modifying the file:

https://github.com/polca/premise/blob/master/premise/data/consequential/leadtimes.yaml

Capital replacement rate

True or False. If False, a horizontal baseline is used. If True, the capital replacement rate is used as baseline. The capital replacement rate is equal to -1 divided by the lifetime (in years) of the technology. It represents the rate at which the capital stock depreciates and must be replaced. Hence, it will be subtracted from the “growth” rate of the technology, to distinguish between the growth rate due to the change in demand and the growth rate due to the replacement of capital stock.

_images/Baseline.png

(left). The capital replacement rate is not considered. (right) The capital replacement rate is subtracted from the growth rate to distinguish between the growth rate due to the change in demand and the growth rate due to the replacement of capital stock.

If you wish to modify the default lifetime values used for the different technologies, you can do so by modifying the file:

https://github.com/polca/premise/blob/master/premise/data/consequential/lifetimes.yaml

Measurement method

Methods 0 and 1 are used if the production volume follows an almost linear pattern. Methods 2, 3 and 4 are used if the production volume follows a non-linear pattern. Short-lasting changes tend to follow a linear pattern, whereas long-lasting changes often do not.

  • 0 = slope: Default method, also used by ecoinvent.

  • 1 = linear regression: Outliers have less of an effect on the results than with Method 0.

  • 2 = area under the curve: Used if there is an emphasis on the consequences in the short term, e.g., if knowing “when” to best introduce the change is important.

  • 3 = weighted slope: Curvature is determined using two slopes. First, the same slope as used in Method 0. Second, a shorter slope, which by default is placed at the end of the time interval. The ratio of the short and long slope is used to adjust the calculated values of Method 0. By placing the shorter slope at the end, exponential growth curves are favored. Used if there is an emphasis on the consequences in the long term, e.g., if the focus of the study is on reaching net zero emissions by 2050.

  • 4 = time interval is split in individual years and measured: The more balanced approach out of the three non-linear methods (i.e., 2, 3, and 4). Short-, mid- and long-term developments are equally important.

_images/Measure_methods.png

Non-linear methods (2, 3 and 4) are used if the production volume follows a non-linear pattern. Short-lasting changes tend to follow a linear pattern, whereas long-lasting changes often do not.

Weighted slope start

Weighted slope start is needed for measurement method 3. The number indicates where the short slope starts and is given as the fraction of the total time interval.

Weighted slope end

Weighted slope end is needed for measurement method 3. The number indicates where the short slope ends and is given as the fraction of the total time interval.

Database creation

The user needs to specify the arguments presented above. If not, the following default arguments value are used:

args = {
    "range time":2,
    "duration":0,
    "foresight":False,
    "lead time":False,
    "capital replacement rate":False,
    "measurement": 0,
    "weighted slope start": 0.75,
    "weighted slope end": 1.00
}
ndb = NewDatabase(
    scenarios = scenarios,
    source_db="ecoinvent 3.8 consequential",
    source_version="3.8",
    key='xxxxxxxxx',
    system_model="consequential",
    system_args=args
)

ndb.update("electricity")

ndb.write_db_to_brightway()

Frequently Asked Questions

Here are some frequently asked questions about premise. If you have a question that is not answered here, please contact us.

Ecoinvent

What is ecoinvent?

Ecoinvent is a database of life cycle inventory data, which is used to calculate the environmental impacts of products and services. It is the most widely used LCI database in the world, and is maintained by the ecoinvent association, in Zurich, Switzerland.

What is the ecoinvent version used in premise?

premise can use the following system models:

  • cut-off

  • consequential

from version 3.6 to 3.9.1.

How does premise use ecoinvent?

premise adds and modifies inventories of the ecoinvent database, to represent the future state of the world, as projected by an Integrated Assessment Model (IAM). It does so by duplicating existing inventories and modifying them to represent the future state of the world. It also adds new inventories, when necessary.

Can I share the modified ecoinvent database?

No. The modified ecoinvent database is a derivative work of the ecoinvent database, and cannot be shared. However, you can share the IAM scenario and the code used to modify the ecoinvent database.

Can I share results obtained with the modified ecoinvent database?

Yes. You can share the results obtained with the modified ecoinvent database.

Can I use the modified ecoinvent database for commercial purposes?

While premise’s license allows its use for commercial purposes, you need to check the ecoinvent license to see if it allows the use of the modified ecoinvent database for commercial purposes.

How can I share modified ecoinvent databases?

premise allows producing “datapackages” that contains the required multiplication factors to be applied to the ecoinvent database, for other users to reproduce the modified ecoinvent database. These datapackages can be shared freely, as they do not contain any ecoinvent data.

IAM models

I use a different IAM than REMIND or IMAGE … Can I still use premise?

There is a MAPPING section in the documentation that explains how to link to a new IAM. The YAML files under ``premise/iam_variables_mapping`` are the main body of files that needs to be changed, to properly establish a correspondence between your IAM variables and the variables used in premise. It is also necessary to provide premise with the geographical definitions of the regions used in your IAM. This is done by providing a .json file with the regions and their corresponding ecoinvent regions. The rest of the code is generic and should work with any IAM.

What columns are necessary in the IAM files?

The code has been refactored since. Any column other than:

  • Region

  • Variable

  • Unit

  • and the variable values for each time step

is ignored.

IAM data collection

How was the list of variables in the mapping files established?

The list of IAM variables and mapping with premise variables has been established through collaboration with developers of IAM models, to ensure that the meaning between each IAM variable corresponds with that of premise.

Is it possible to expand this list? (e.g. agriculture crops for energy)

It is certainly possible to extend this list. You would however need to extend premise’s code to tell it what to do with these additional variables. For example, if you want to use the IAM output for integrating projections that relate to agriculture crops for energy, you would need to write a module in premise (e.g., energy_crops.py) that would perform a series of modifications on the LCA datasets, just like other modules do.

Is the unit and the description of these parameters documented? Or are they necessarily the same as the ones of the ecoinvent datasets they refer to?

They are now documented, under the MAPPING section. There are essentially two types of variables:

  • variables that relate to production volumes of technologies, which units must represent a production volume over time (e.g., GWh/year)

  • variables that relate to the efficiency of technologies, which is unitless, or represented by an efficiency ratio (e.g., %)

What if a variable in premise corresponds to several variables in the IAM?

We have not really seen that case yet. In any case, mapping one IAM variable to two premise variables is possible (whether it is methodologically correct is a question left to your appreciation).

Regionalization

Are datasets regionalized on the basis of the IAM scenario only, or does it come from other sources?

premise tries to limit the use of external sources of data. At the moment, the only sources of data, other than those from the IAM scenario, used for projections are:

  • efficiency values for different photovoltaic panels (taken from the Fraunhofer ISE database)

  • emissions factors for local air pollution (taken from the GAINS-EU and GAINS-IAM databases)

Hence, the regionalization of datasets is based on the IAM scenario only.

Does premise generate more regionalised datasets than in original EI3.x database?

Yes. premise generates regionalized datasets for all regions in the IAM model, for each technology for which a IAM-to-premise correspondence is provided, if not already existing in the Ecoinvent database. For example, if the IAM model considers technology A over 10 regions, premise collects datasets in the ecoinvent database (or imported inventories) that represent technology A and duplicates it for each region. Sometimes, only one dataset is available in the ecoinvent database, in which case premise duplicates it 10 times. Other times, several datasets are available (ie.g., in FR, CN and RoW), in which case premise uses the French dataset for the European region, the Chinese dataset for the Chinese region, and the RoW dataset for the other IAM regions. Then, premise proceeds to regionalize these datasets by finding the most appropriate inputs suppliers for each duplicated dataset.

How does premise handle the different granularities between the IAM regions and the Ecoinvent regions?

premise simply uses the correspondence between IAM regions and Ecoinvent regions (which are, most of the time defined by ISO alpha-2 country codes), often provided by the IAM developers.

For example, the REMIND REF region is associated with the following ecoinvent regions:

  • AM

  • AZ

  • BY

  • GE

  • KZ

  • KG

  • MD

  • RU

  • TJ

  • TM

  • UA

  • UZ

If a technology needs to be included within a market for that region (e.g., coal-based electricity), premise looks for datasets for that technology (e.g., electricity production, hard coal) in the ecoinvent database that are located in any of these above-listed locations, and calculates supply shares based on the production volumes information provided in each of these datasets (i.e., under the production volumes field). Hence, coal-based electricity in the REF electricity market is supplied by several coal-based electricity datasets, each of which is located in a different country (see list above) according to their current production volumes. This approach highlights a limitation, where current production volumes are used to calculate supply mix for a given technology within a given IAM region.

Consistency with climate targets

How do we ensure consistency between IAM scenario and pLCA results (in terms of global warming / temperature increase)?

In theory, there is consistency between the IAM scenario and pLCA database when 100% of the IAM variables and related projections are integrated into the pLCA database.

This is not the case today, as premise only integrates a subset of IAM variables, notably those that relate to:

  • power production

  • steel production

  • cement production

  • fuel production

  • transport

Hence, important sectors are still left out, such as:

  • agriculture

  • heat

  • chemicals

  • paper

Also, sectors that are considered by premise are not fully or perfectly integrated, as:

  • some IAM variables are sometimes not available (e.g., efficiency).

  • some IAM variables are sometimes not considered by premise (e.g., fuel mix for cement production)

Hence, premise-generated databases are not fully consistent with the IAM scenario, including its climate target. If an ambitious climate target is considered, the use of premise-generated databases probably leads to an overestimate of GHG emissions, since sectors that are expected to under mitigation measures are left unchanged. It will however mostly depend on the product system you analyze.

Additional inventories

Can additional inventories be modelled with parameters? If so, how are they used?

Additional inventories (imported as such or via data packages) can be modelled with (brightway2) parameters, but those will not be considered by premise.

Can some parameters of the additional inventories be made scenario- and time-dependant?

Yes, via the use of data packages. Data packages allow to package additional scenarios to be considered in addition to the global IAM scenario. With data packages, it is possible to map the efficiency of processes to a variable. That variable can vary over time and across scenarios. Besides efficiency, it is also possible to change a market mix, distribution losses or any other aspects, of a product’s supply chain, via the use of variables in data packages.

Can premise manage an efficiency evolution for the additional inventories?

Yes, via the use of data packages (see User-defined scenarios section). It is possible to map the efficiency of processes to a variable. That variable can vary over time and across scenarios.

Efficiency adjustments

Is the calculated scaling factor (ratio of efficiencies in year 20XX vs 2020) applied to all inputs of the transformed dataset, or only to the energy feedstock input?

It depends on the nature of the process. For energy conversion processes (e.g., power generation), all inputs are scaled up or down. For processes that convert energy and material (e.g., cement or steel production), only the inputs that relate to energy (e.g., fuel, electricity) inputs are scaled up or down, the input of material remaining unchanged.

What happens if the IAM does not provide efficiencies for certain processes?

They will be ignored and the efficiency of said process wil not be adjusted.

Why use external data sources for PV efficiency, rather than the output of IAM?

Efficiency values for photovoltaic panels are not always provided by IAM scenarios. When they are, they are often constant (i.e., the efficiency does not increase over time). This can become an issue when they represent a significant share of the electricity mix. Hence, at the moment, we use external sources to document the projected efficiency of photovoltaic modules. A venue of improvement may be to use IAM efficiency variables for photovoltaic panels when available, and fall back on external sources if not.