meta data for this page
Differences
This shows you the differences between two versions of the page.
Both sides previous revisionPrevious revisionNext revision | Previous revisionNext revisionBoth sides next revision | ||
sector:ippu:mineral_industry:cement_production:start [2021/12/20 10:35] – [Table] kludt | sector:ippu:mineral_industry:cement_production:start [2023/04/06 09:30] – [Emission factors] kludt | ||
---|---|---|---|
Line 3: | Line 3: | ||
===== Short description ===== | ===== Short description ===== | ||
- | ^ Category Code ^ Method | + | ^ Category Code ^ Method |
- | | 2.A.1 | + | | 2.A.1 | T1 |
- | ^ | + | ^ |
- | | 2.A.1 | -/- | -/- | -/- | -/- | - | - | -/- | | + | | Key Category: |
{{page> | {{page> | ||
\\ | \\ | ||
Line 27: | Line 27: | ||
==== Emission factors ==== | ==== Emission factors ==== | ||
- | The emission factors used for emissions calculation are based on figures from research projects as well as from expert judgements. | + | The emission factors used for emissions calculation are based on figures from research projects |
In the German cement industry, dust separated from clinker burning exhaust gas is returned to the burning process. As a result, there is no need to take account of significant losses of particles via the exhaust-gas pathway. - On the other hand, particulate matter emissions occur during clinker grinding. | In the German cement industry, dust separated from clinker burning exhaust gas is returned to the burning process. As a result, there is no need to take account of significant losses of particles via the exhaust-gas pathway. - On the other hand, particulate matter emissions occur during clinker grinding. | ||
Line 34: | Line 34: | ||
__Table 1: Overview of applied emission factors__ | __Table 1: Overview of applied emission factors__ | ||
- | ^ Pollutant | + | ^ |
- | ^ NOₓ || clinker burning | + | ^ NO< |
- | ^ SO₂ || clinker burning | + | ^ SO< |
- | ^ NMVOC || clinker burning | + | ^ NMVOC |
- | ^ NH₃ || clinker burning | + | ^ NH< |
- | ^ Hg || clinker burning | + | ^ Hg | ::: |
- | ^ Pb || clinker burning | + | ^ Pb | ::: |
- | ^ Cd || clinker burning | + | ^ Cd | ::: |
- | ^ PCB || clinker burning | + | ^ PCB |
- | ^ PCDD || clinker burning | + | ^ PCDD | ::: |
- | ^ B(a)P || clinker burning | + | ^ B(a)P * | ::: |
- | ^ PAH 1-4 1) || clinker burning | + | ^ PAH-16 * * |
- | ^ PAH 16 || clinker burning | + | ^ // |
- | ^ // | + | ^ //PM< |
- | ^ //PM₁₀// || //clinker grinding// | + | ^ //PM< |
- | ^ //PM₂.₅// | + | |
- | The data for PAH 1-4 in NFR-Tables only shows the sum of the available 1-4 PAHs, in this case only of BaP. | + | * The data for PAH 1-4 in NFR-Tables only shows the sum of the available 1-4 PAHs, in this case only of BaP. |
- | Outside NFR-Tables a different PAH mixture is known, as a result of research for EPA-PAH (PAH16-Standard). | + | |
+ | * * Outside NFR-Tables a different PAH mixture is known, as a result of research for EPA-PAH (PAH16-Standard). | ||
Emissions of HCB are not applicable according to a research result. The table of EF is related to two different AD sets. For purposes of the most pollutants the AD is burnt clinker. For purposes of emission estimation of PM the AD is grinded clinker (included further materials as domestic burnt clinker). NFR tables could provide only one AD (burnt clinker). | Emissions of HCB are not applicable according to a research result. The table of EF is related to two different AD sets. For purposes of the most pollutants the AD is burnt clinker. For purposes of emission estimation of PM the AD is grinded clinker (included further materials as domestic burnt clinker). NFR tables could provide only one AD (burnt clinker). | ||
Line 63: | Line 63: | ||
===== Recalculations ===== | ===== Recalculations ===== | ||
- | With **activity data** and **emission factors** remaining unrevised, no recalculations have been carried out compared to last year's submission. | + | Recalculations were necessary due to updated emission factors for all years. The significant changes can be shown as an absolute difference over time as follows: |
+ | |||
+ | [{{: | ||
+ | |||
+ | But since data for PAH 1-4 in NFR-Tables only shows the sum of the available four PAHs, only BaP and the value for PAH 1-4 have decreased strongly. Please see the EF chapter, too. | ||
<WRAP center round info 60%> | <WRAP center round info 60%> | ||
- | For pollutant-specific information on recalculated emission estimates for Base Year and 2018, please see the pollutant specific recalculation tables following [[general: | + | For **pollutant-specific information on recalculated emission estimates for Base Year and 2020**, please see the pollutant specific recalculation tables following [[general: |
</ | </ | ||
===== Planned improvements ===== | ===== Planned improvements ===== | ||
- | For purposes of updating the EF project has started in 2019, but results | + | No improvements |