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Process Data set: ACBFS - Air-Cooled Blast Furnace Slag (en) en

Key Data Set Information
Location DE
Geographical representativeness description European Union
Name
ACBFS - Air-Cooled Blast Furnace Slag
General comment on data set This representative EPD covers air-cooled blast furnace slag (ACBFS), a crystalline by-product formed during the slow cooling of molten blast furnace slag under atmospheric conditions. Once solidified, ACBFS appears as a coarse-grained, rock-like material and is primarily used as a mineral aggregate in the construction industry – for example, in base layers, backfills, or asphalt mixtures. Its use is governed by the applicable standards: EN 12620 – Aggregates for concrete EN 13242 – Aggregates for unbound and hydraulically bound materials for use in civil engineering work and road construction The specific application of the product is subject to the respective national legal regulations at the place of use, particularly regarding environmental compatibility, installation classes, and approval procedures. The production of ACBFS takes place as part of the pig iron manufacturing process in the blast furnace. Iron-bearing input materials (sinter, pellets, ores) are charged into the furnace along with coke. The uniform composition of this charge significantly influences the chemical composition of the resulting slag. ACBFS can be recycled and reused after (every) excavation. According to the German Substitute Building Materials Ordinance (EBV), ACBFS is classified as HOS 1. Key parameters: pH value: 9–12 Electrical conductivity (µS/cm): < 5000 SO₄ (mg/l): < 1300 Typical chemical composition (by mass %): Chemical compoundAverage value [%]Fe total0.5CaO42SiO₂34MgO7.2Al₂O₃10 The primary data represent iron and steel production in Germany. The quality level of geographical representativity can be considered “good,” the quality level of technical representativity can be considered “good,” and the temporal representativity can also be considered “good.” Therefore, the overall data quality for this EPD can be classified as “good.” To ensure comparability of results, only consistent background data from the ecoinvent database version 3.9.1 was used in the life cycle assessment (e.g. datasets for energy, transport, auxiliary and operating materials), which refer to the reference year 2022. The database is regularly reviewed and thus meets the requirements of EN 15804 (background data not older than 10 years). All consistent datasets contained in the ecoinvent database are documented and can be accessed in the ecoinvent online documentation. For ACBFS, only modules A1–A3 are declared since the material is integrated into other construction products (e.g., cement, concrete) and cannot be physically separated or identified at end of life.
Copyright Yes
Owner of data set
Quantitative reference
Reference flow(s)
Biogenic carbon content
  • Carbon content (biogenic): 0.0 kg
  • Carbon content (biogenic) - packaging: 0.0 kg
Time representativeness
Data set valid until 2030
Time representativeness description All primary data were collected during the accounting period (01.01.2023 – 31.12.2023).All secondary data were selected with a geographical reference to Germany whenever possible.If datasets with a reference to Germany were not available, datasets were chosen based on the following geographical scope, in descending order: Europe, Global.
Technological representativeness
Technology description including background system Construction phase is outside the scope of the declaration.
Flow diagram(s) or picture(s)
  • Product Picture Image

Indicators of life cycle

IndicatorDirectionUnit Raw material supply
A1
Production
A1-A3
Transport
A2
Manufacturing
A3
Input
  • 0.1155
  • 0.5657
  • 0.01372
  • 0.4364
Input
  • 0
  • 0
  • 0
  • 0
Input
  • 6.196
  • 44.98
  • 1.033
  • 37.75
Input
  • 0
  • 0
  • 0
  • 0
Input
  • 0
  • 0
  • 0
  • 0
Input
  • 0
  • 0
  • 0
  • 0
Input
  • 0.0003383
  • 0.02577
  • 0.0001246
  • 0.02531
Output
  • 999.2
  • 999.2
  • 0.000005299
  • 0.00004846
Output
  • 0.06734
  • 0.1833
  • 0.007098
  • 0.1089
Output
  • 9.712E-7
  • 0.0001477
  • 2.827E-7
  • 0.0001464
Output
  • 0
  • 0
  • 0
  • 0
Output
  • 0
  • 0
  • 0
  • 0
Output
  • 0
  • 0
  • 0
  • 0
Output
  • 0
  • 0
  • 0
  • 0
Output
  • 0
  • 0
  • 0
  • 0

IndicatorUnit Raw material supply
A1
Production
A1-A3
Transport
A2
Manufacturing
A3
  • 6.196
  • 44.98
  • 1.033
  • 37.75
  • 6.29E-7
  • 0.00001363
  • 1.115E-7
  • 0.00001289
  • 0.0008025
  • 0.009404
  • 0.001959
  • 0.006642
  • 1.865E-9
  • 3.162E-8
  • 1.276E-9
  • 2.848E-8
  • 0.000009153
  • 0.0001325
  • 5.4E-7
  • 0.0001228
  • 0.0002086
  • 0.001962
  • 0.0004679
  • 0.001285
  • 0.002409
  • 0.0225
  • 0.005183
  • 0.01491
  • 0.0007802
  • 0.006774
  • 0.001443
  • 0.004551
  • 0.00007517
  • 0.0008162
  • 0.00002518
  • 0.0007158
  • 0.1573
  • 2.929
  • 0.08337
  • 2.689
  • 0.00007082
  • 0.0005546
  • 0.0001015
  • 0.0003823
  • 0.1574
  • 2.931
  • 0.08349
  • 2.69
  • 0.004502
  • 0.1833
  • 0.003291
  • 0.1755

IndicatorUnit Raw material supply
A1
Production
A1-A3
Transport
A2
Manufacturing
A3
1This impact category deals mainly with the eventual impact of low dose ionizing radiation on human health of the nuclear fuel cycle. It does not consider effects due to possible nuclear accidents, occupational exposure nor due to radioactive waste disposal in underground facilities. Potential ionizing radiation from the soil, from radon and from some construction materials is also not measured by this indicator.
2The results of this environmental impact indicator shall be used with care as the uncertainties on these results are high or as there is limited experiences with the indicator.
Potential Comparative Toxic Unit for ecosystems (ETP-fw) 2
  • 1.77
  • 8.436
  • 0.5196
  • 6.147
Potential Comparative Toxic Unit for humans - cancer effects (HTP-c) 2
  • 1.261E-9
  • 1.967E-9
  • 4.296E-11
  • 6.629E-10
Potential Comparative Toxic Unit for humans - non-cancer effects (HTP-nc) 2
  • 7.854E-10
  • 3.126E-8
  • 3.605E-10
  • 3.011E-8
Potential Human exposure efficiency relative to U235 (IRP) 1
  • 0.001414
  • 0.1143
  • 0.0004355
  • 0.1125
Potential Soil quality index (SQP) 2
  • 0.8181
  • 4.279
  • 0.1953
  • 3.266
Potential incidence of disease due to PM emissions (PM) 2
  • 7.114E-9
  • 3.284E-8
  • 2.807E-9
  • 2.291E-8