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* Add emissions and fuel consumption from fuel refinieries * [pre-commit.ci] auto fixes from pre-commit.com hooks for more information, see https://pre-commit.ci --------- Co-authored-by: pre-commit-ci[bot] <66853113+pre-commit-ci[bot]@users.noreply.github.com>
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1 | Unit | Values | Description | |
---|---|---|---|---|
2 | St_primary_fraction | -- | Dictionary with planning horizons as keys. | The fraction of steel produced via primary route versus secondary route (scrap+EAF). Current fraction is 0.6 |
3 | DRI_fraction | -- | Dictionary with planning horizons as keys. | The fraction of the primary route DRI + EAF |
4 | ||||
5 | H2_DRI | -- | float | The hydrogen consumption in Direct Reduced Iron (DRI) Mwh_H2 LHV/ton_Steel from 51kgH2/tSt in `Vogl et al (2018) <https://doi.org/10.1016/j.jclepro.2018.08.279>`_ |
6 | elec_DRI | MWh/tSt | float | The electricity consumed in Direct Reduced Iron (DRI) shaft. From `HYBRIT brochure <https://ssabwebsitecdn.azureedge.net/-/media/hybrit/files/hybrit_brochure.pdf>`_ |
7 | Al_primary_fraction | -- | Dictionary with planning horizons as keys. | The fraction of aluminium produced via the primary route versus scrap. Current fraction is 0.4 |
8 | MWh_NH3_per_tNH3 | LHV | float | The energy amount per ton of ammonia. |
9 | MWh_CH4_per_tNH3_SMR | -- | float | The energy amount of methane needed to produce a ton of ammonia using steam methane reforming (SMR). Value derived from 2012's demand from `Center for European Policy Studies (2008) <https://ec.europa.eu/docsroom/documents/4165/attachments/1/translations/en/renditions/pdf>`_ |
10 | MWh_elec_per_tNH3_SMR | -- | float | The energy amount of electricity needed to produce a ton of ammonia using steam methane reforming (SMR). same source, assuming 94-6% split methane-elec of total energy demand 11.5 MWh/tNH3 |
11 | Mwh_H2_per_tNH3 _electrolysis | -- | float | The energy amount of hydrogen needed to produce a ton of ammonia using Haber–Bosch process. From `Wang et al (2018) <https://doi.org/10.1016/j.joule.2018.04.017>`_, Base value assumed around 0.197 tH2/tHN3 (>3/17 since some H2 lost and used for energy) |
12 | Mwh_elec_per_tNH3 _electrolysis | -- | float | The energy amount of electricity needed to produce a ton of ammonia using Haber–Bosch process. From `Wang et al (2018) <https://doi.org/10.1016/j.joule.2018.04.017>`_, Table 13 (air separation and HB) |
13 | Mwh_NH3_per_MWh _H2_cracker | -- | float | The energy amount of amonia needed to produce an energy amount hydrogen using ammonia cracker |
14 | NH3_process_emissions | MtCO2/a | float | The emission of ammonia production from steam methane reforming (SMR). From UNFCCC for 2015 for EU28 |
15 | petrochemical_process _emissions | MtCO2/a | float | The emission of petrochemical production. From UNFCCC for 2015 for EU28 |
16 | HVC_primary_fraction | -- | float | The fraction of high value chemicals (HVC) produced via primary route |
17 | HVC_mechanical_recycling _fraction | -- | float | The fraction of high value chemicals (HVC) produced using mechanical recycling |
18 | HVC_chemical_recycling _fraction | -- | float | The fraction of high value chemicals (HVC) produced using chemical recycling |
19 | HVC_environment_sequestration_fraction | -- | float | The fraction of high value chemicals (HVC) put into landfill resulting in additional carbon sequestration. The default value is 0. |
20 | waste_to_energy | -- | bool | Switch to enable expansion of waste to energy CHPs for conversion of plastics. Default is false. |
21 | waste_to_energy_cc | -- | bool | Switch to enable expansion of waste to energy CHPs for conversion of plastics with carbon capture. Default is false. |
22 | ||||
23 | sector_ratios_fraction_future | -- | Dictionary with planning horizons as keys. | The fraction of total progress in fuel and process switching achieved in the industry sector. |
24 | basic_chemicals_without_NH3_production_today | Mt/a | float | The amount of basic chemicals produced without ammonia (= 86 Mtethylene-equiv - 17 MtNH3). |
25 | HVC_production_today | MtHVC/a | float | The amount of high value chemicals (HVC) produced. This includes ethylene, propylene and BTX. From `DECHEMA (2017) <https://dechema.de/dechema_media/Downloads/Positionspapiere/Technology_study_Low_carbon_energy_and_feedstock_for_the_European_chemical_industry-p-20002750.pdf>`_, Figure 16, page 107 |
26 | Mwh_elec_per_tHVC _mechanical_recycling | MWh/tHVC | float | The energy amount of electricity needed to produce a ton of high value chemical (HVC) using mechanical recycling. From SI of `Meys et al (2020) <https://doi.org/10.1016/j.resconrec.2020.105010>`_, Table S5, for HDPE, PP, PS, PET. LDPE would be 0.756. |
27 | Mwh_elec_per_tHVC _chemical_recycling | MWh/tHVC | float | The energy amount of electricity needed to produce a ton of high value chemical (HVC) using chemical recycling. The default value is based on pyrolysis and electric steam cracking. From `Material Economics (2019) <https://materialeconomics.com/latest-updates/industrial-transformation-2050>`_, page 125 |
28 | ||||
29 | chlorine_production _today | MtCl/a | float | The amount of chlorine produced. From `DECHEMA (2017) <https://dechema.de/dechema_media/Downloads/Positionspapiere/Technology_study_Low_carbon_energy_and_feedstock_for_the_European_chemical_industry-p-20002750.pdf>`_, Table 7, page 43 |
30 | MWh_elec_per_tCl | MWh/tCl | float | The energy amount of electricity needed to produce a ton of chlorine. From `DECHEMA (2017) <https://dechema.de/dechema_media/Downloads/Positionspapiere/Technology_study_Low_carbon_energy_and_feedstock_for_the_European_chemical_industry-p-20002750.pdf>`_, Table 6 page 43 |
31 | MWh_H2_per_tCl | MWhH2/tCl | float | The energy amount of hydrogen needed to produce a ton of chlorine. The value is negative since hydrogen produced in chloralkali process. From `DECHEMA (2017) <https://dechema.de/dechema_media/Downloads/Positionspapiere/Technology_study_Low_carbon_energy_and_feedstock_for_the_European_chemical_industry-p-20002750.pdf>`_, page 43 |
32 | methanol_production _today | MtMeOH/a | float | The amount of methanol produced. From `DECHEMA (2017) <https://dechema.de/dechema_media/Downloads/Positionspapiere/Technology_study_Low_carbon_energy_and_feedstock_for_the_European_chemical_industry-p-20002750.pdf>`_, page 62 |
33 | MWh_elec_per_tMeOH | MWh/tMeOH | float | The energy amount of electricity needed to produce a ton of methanol. From `DECHEMA (2017) <https://dechema.de/dechema_media/Downloads/Positionspapiere/Technology_study_Low_carbon_energy_and_feedstock_for_the_European_chemical_industry-p-20002750.pdf>`_, Table 14, page 65 |
34 | MWh_CH4_per_tMeOH | MWhCH4/tMeOH | float | The energy amount of methane needed to produce a ton of methanol. From `DECHEMA (2017) <https://dechema.de/dechema_media/Downloads/Positionspapiere/Technology_study_Low_carbon_energy_and_feedstock_for_the_European_chemical_industry-p-20002750.pdf>`_, Table 14, page 65 |
35 | MWh_MeOH_per_tMeOH | LHV | float | The energy amount per ton of methanol. From `DECHEMA (2017) <https://dechema.de/dechema_media/Downloads/Positionspapiere/Technology_study_Low_carbon_energy_and_feedstock_for_the_European_chemical_industry-p-20002750.pdf>`_, page 74. |
36 | hotmaps_locate_missing | -- | {true,false} | Locate industrial sites without valid locations based on city and countries. |
37 | reference_year | year | YYYY | The year used as the baseline for industrial energy demand and production. Data extracted from `JRC-IDEES 2015 <https://data.jrc.ec.europa.eu/dataset/jrc-10110-10001>`_ |
38 | oil_refining_emissions | tCO2/MWh | float | The emissions from oil fuel processing (e.g. oil in petrochemical refinieries). The default value of 0.013 tCO2/MWh is based on DE statistics for 2019; the EU value is very similar. |