h1

h2

h3

h4

h5
h6
% IMPORTANT: The following is UTF-8 encoded.  This means that in the presence
% of non-ASCII characters, it will not work with BibTeX 0.99 or older.
% Instead, you should use an up-to-date BibTeX implementation like “bibtex8” or
% “biber”.

@PHDTHESIS{Suer:963309,
      author       = {Suer, Julian},
      othercontributors = {Traverso, Marzia and Deike, Rüdiger},
      title        = {{G}reen steel - life cycle modeling of an integrated steel
                      site : carbon footprint and energy transformation analysis
                      of decarbonized steel production},
      school       = {Rheinisch-Westfälische Technische Hochschule Aachen},
      type         = {Dissertation},
      address      = {Aachen},
      publisher    = {RWTH Aachen University},
      reportid     = {RWTH-2023-07732},
      pages        = {1 Online-Ressource : Illustrationen, Diagramme},
      year         = {2023},
      note         = {Veröffentlicht auf dem Publikationsserver der RWTH Aachen
                      University; Dissertation, Rheinisch-Westfälische Technische
                      Hochschule Aachen, 2023, Kumulative Dissertation},
      abstract     = {The steel industry is focused on reducing its environmental
                      impact. Steel is typically produced primarily from iron ores
                      in integrated sites and secondarily from scrap recycling in
                      electric arc furnaces (EAF). Traditional integrated sites
                      include hot metal generation via the blast furnace route,
                      basic oxygen steelmaking (BOF), continuous casting, and
                      subsequent hot-rolling. For the evaluation of environmental
                      impacts generated by the product, the life cycle assessment
                      (LCA) methodology according to ISO 14040/44 has been used.
                      The LCA is internationally recognized and standardized.
                      Using the LCA methodology, the impacts of primary steel
                      production via the blast furnace route and the secondary
                      scrap-based steel production via the EAF route are assessed.
                      These production routes represent the state-of-the art.
                      Subsequently, decarbonization strategies are analysed using
                      the product carbon footprint (PCF) methodology according to
                      ISO 14067. In a blast furnace coal and coke are used for the
                      reduction and melting of iron ores. The decarbonization of
                      the steel industry requires a shift from a coal-based
                      metallurgy towards a hydrogen and electricity-based steel
                      production, or purely electric, if the utilized hydrogen
                      stems from electrolysis. The blast furnace can be
                      substituted by direct reduction (DR) plants with subsequent
                      electrical melting. In DR plants, iron oxides can be reduced
                      by natural gas as well as pure hydrogen. DR plants have
                      reached capacities, which allow replacing blast furnaces on
                      a direct basis. While the majority of European steel
                      producers have pointed to direct reduced iron (DRI)
                      production as a key part of their decarbonization targets,
                      the next steps are highly discussed. Two main routes stand
                      out: (1) Melting and processing the DRI in an EAF directly
                      to crude steel; (2) Melting and carburizing the DRI in an
                      electric melting unit to hot metal. The hot metal is then
                      further refined in a BOF to crude steel. Whereas the first
                      route seems to be more straightforward, some metallurgical
                      points require discussion. On the basis of the carbon
                      footprint methodology different scenarios of a stepwise
                      transition are evaluated and values of possible
                      CO2equivalent (CO2eq) reduction are coupled with the demand
                      of hydrogen, electricity, natural gas, and coal. For
                      example, while the traditional blast furnace - BOF route
                      delivers a surplus of electricity in the range of 0.7 MJ/kg
                      hot-rolled coil; this surplus turns into a deficit of about
                      17 MJ/kg hot-rolled coil for a hydrogen-based steel
                      production route. On the other hand, while the product
                      carbon footprint of the blast furnace-related production
                      route is 2.1 kg CO2eq/kg hot-rolled coil; this footprint can
                      be reduced to 0.75 kg CO2eq/kg hot-rolled coil for the
                      hydrogen-related route, obtained with electricity input
                      generated by renewable sources. Thereby the direct impact of
                      the processes of the integrated site can even be reduced to
                      0.15 kg CO2eq/kg hotrolled coil. The remaining carbon
                      footprint is caused by upstream processes for which no
                      improvements are considered. However, if the electricity
                      input has a carbon footprint related to the German or
                      European electricity grid mix, the respective carbon
                      footprint of hot-rolled coil increases up to 3.0 kg CO2eq/kg
                      hot-rolled coil. A natural gas-based DR production route
                      leads to a carbon footprint of 1.4 - 1.7 kg CO2eq/kg
                      hot-rolled coil, depending on the electricity mix used for
                      the steel production processes. A detailed break-even
                      analysis is given, comparing the use of natural gas and
                      hydrogen using different electricity mixes. Intermediate
                      scenarios can enable a stepwise transition of changed plant
                      configurations and material and energy related feedstocks.
                      Simultaneously, the intermediate scenarios lead to PCF
                      reductions in time. In this dissertation the scenarios
                      hydrogen and natural gas injection into a blast furnace and
                      the use of hot briquetted iron (HBI) in a blast furnace are
                      analyzed.},
      cin          = {316710},
      ddc          = {624},
      cid          = {$I:(DE-82)316710_20180607$},
      typ          = {PUB:(DE-HGF)11},
      doi          = {10.18154/RWTH-2023-07732},
      url          = {https://publications.rwth-aachen.de/record/963309},
}