2.C.1 - Iron & Steel Production

The source subcategory NFR 2.C.1 - Iron & Steel Production comprises process-related emissions from oxygen steel and electric steel production.

In 2023, a total of 25.6 million tonnes of raw steel were produced in six integrated steelworks. Electrical steel production amounted to another 9,8 million tonnes.

Other structural elements are sinter production, hot iron production, hot rolling, iron and steel foundries (including malleable casting). The last Siemens-Martin steelworks (Stahlwerk Brandenburg) was shut down shortly after 1990. The last Thomas steelworks (Maxhütte Sulzbach-Rosenberg) discontinued its production in 2002. Due to their minor relevance and their phase-out, the emissions from Siemens-Martin and Thomas steel production are jointly calculated with the emissions from oxygen steel production.

Energy-related emissions from steel production for the years 1990 to 1994 (for individual pollutants until 1999) are reported under 1.A Fuel combustions in the respective subcategory 1.A.2.a. A detailed explanation for the individual pollutants is also found there.

Activity data is collected from plant operators by national institutions. Since the discontinuation of the special public statistics for iron and steel production (FS. 4, R. 8.1), the information is collected by the German steel trade association Wirtschaftsvereinigung Stahl (WV Stahl) based on a formal agreement.

In the iron and steel industry, only minor amounts of secondary fuels are used for pig iron production in individual blast furnaces. They are used as substitute reducing agents of coke and coal. To date, these materials have not yet been included in the national statistics nor in the Energy Balance. For this reason, the data used is also provided by WV Stahl.

The emission factors used to calculate emissions are based on emission data from individual plants. The emission factors for 1995 to 2001 were determined by the German Environment Agency (UBA for its initials in German) itself and those for 2008 and later through a research project¹⁾.

As the EF for the years 1995 to 2001 as well as for 2008 are based on real stack emission data. Since both combustion and process-related emissions are released through the same stacks, emission factors could not be calculated individually for combustion or process-related emissions. Hence, wherever plant-based EF were availaible, as it the case for most pollutants for the years 1995 and later, all emissions are reported under 2.C.1.

Please note that the reported emissions also cover diffuse emissions from sources that are not covered in the EMEP/EEA Guidebook. For many pollutants and sources, individual EFs for channelled as well as diffuse emissions have been determined. While there is sufficient knowledge and measurement data of channelled emissions, the emission data concerning diffuse sources is usually based on estimations using parameters adapted to the local conditions of the individual emission source. Therefore, emission data for one source of diffuse emissions is not significant for the diffuse emissions from other plants. The emission factors given below were calculated as the weighted average of the pollution loads reported by the plant operators for individual diffuse sources, in relation to their corresponding production amounts.

Table 1: Overview of the emission factors applied for sinter production

Table 2: Overview of the emission factors applied for pig iron production

Table 3: Overview of the emission factors applied for oxygen steel production

Table 4: Overview of the emission factors applied for electric steel production

Table 5: Overview of the emission factors applied for hot and cold rolling

Table 6: Overview of the emission factors applied for iron and steel casting

HCB

For the calculation of HCB emissions in sinter production, the standard emission factor is used. By implementing the EMEP/EEA Guidebook standard emission factor, Germany is following recommendations provided by the Expert Review Team for the NECD-Review in 2020.

PAH

In the 2021 review the application of a consistent methodology in reporting of PAH emissions in 2C1-iron and steel production was claimed. As there was not enough data available to report individual PAHs Germany decided to only report total-PAHs for the whole time. Therefore a national total-PAH emission factor for pig iron production was needed as the national inventory solely included BaP emissions for that source.
Emissions of PAH depend on the coating material used. As tar-free materials are used for coating and the blast furnace gas is conducted and used PAH emissions should not play any role. But as PAH emissions could not be surely ruled out and in order to avoid an underestimation of PAH emissions in pig iron production the emission factor for total-PAH is set to the 10-fold of the BaP emission factor following a conservative ansatz and not changing the overall PAH emission trend.

The trends in emissions correspond to the trends of emission factors given in the tables above, which are often driven by regulatory measures.
However, since 2010, the main driver of the emission trends in most cases is the activity data.

Recalculations were necessary for 2022 due to the implementation of the now finalised National Energy Balance.

no improvements planned.