meta data for this page
Differences
This shows you the differences between two versions of the page.
Next revision | Previous revision | ||
sector:ippu:other_solvent_and_product_use:chemical_products:start [2023/03/14 12:51] – [Recalculations] kotzulla | sector:ippu:other_solvent_and_product_use:chemical_products:start [2023/06/27 08:47] (current) – [Method] kotzulla | ||
---|---|---|---|
Line 44: | Line 44: | ||
* The VOC concentrations in these products (substances and preparations), | * The VOC concentrations in these products (substances and preparations), | ||
* The relevant application and emission conditions (or the resulting specific emission factor). | * The relevant application and emission conditions (or the resulting specific emission factor). | ||
+ | |||
The quantity of the solvent-based (pre-)product corresponds to the domestic consumption which is the sum of domestic production plus import minus export. | The quantity of the solvent-based (pre-)product corresponds to the domestic consumption which is the sum of domestic production plus import minus export. | ||
- | || NMVOC Emission | + | <WRAP center round info 55%> |
+ | EM< | ||
+ | </ | ||
The calculated NMVOC emissions of different product groups for a source category are then aggregated. | The calculated NMVOC emissions of different product groups for a source category are then aggregated. | ||
Line 60: | Line 63: | ||
Total emissions of NMVOC emissions of 2.D.3g remain relatively stable. In some major activities amounts of NMVOC emissions raised, such as from solvents used in polystyrene foam processing and the manufacture of solvent-based consumer products. | Total emissions of NMVOC emissions of 2.D.3g remain relatively stable. In some major activities amounts of NMVOC emissions raised, such as from solvents used in polystyrene foam processing and the manufacture of solvent-based consumer products. | ||
- | ===== Uncertainties ===== | ||
- | Emission factors: Relative error rates at ±15% and ±25% (Adhesive manufacturing, | + | ------------------------------- |
+ | ===== Bitumen blowing ===== | ||
+ | === Method === | ||
+ | Bitumen used for road paving, roof coating and other application like pipe sealing needs some enhanced properties that can be achieved by air blowing. | ||
+ | In the GB 2019 < | ||
+ | == Activity data == | ||
+ | The applicable quantities of treated bitumen are calculated from the total-bitumen-production figures published annually by the Federal Office of Economics and Export Control (BAFA), in its official mineral-oil data (Amtliche Mineralöldaten)< | ||
+ | == Emission factors == | ||
+ | |||
+ | The NMVOC and PAH emissions that result from bitumen blowing are calculated with an emission factor derived from the uncontrolled standard emission factor of the GB 2019 taking account of the maximum permitted levels and reduction-measures requirements specified in the Technical Instructions on Air Quality Control (TA Luft). The emission factors for Cd, Cr and Ni were taken from real measurements with an increased safety factor (maximum or ten-fold). | ||
+ | All emission factors remain constant for all years in question. | ||
+ | |||
+ | __Table 1: Overview of the tier-2 emission factors applied for bitumen blowing with post-combustion__ | ||
+ | |||
+ | | ^ EF 2010 ^ Unit ^ Trend ^ | ||
+ | ^ NMVOC | 27.20 | g/t | ||
+ | ^ TSP | 10.00 | g/t | ||
+ | ^ Cd | ||
+ | ^ As | ||
+ | ^ Cr | ||
+ | ^ Ni | ||
+ | ^ Se | ||
+ | ^ PAH | | ||
+ | |||
+ | === Trend discussion (for key categories) === | ||
+ | |||
+ | All trends in emissions correspond to trends of emission factors in table above and of production development. No rising trends are to identify. | ||
+ | |||
+ | [{{sector: | ||
+ | |||
+ | ------------------------------- | ||
+ | |||
+ | ===== Uncertainties ===== | ||
+ | |||
+ | Emission factors: Relative error rates at ±15% and ±25% (Adhesive manufacturing, | ||
===== Recalculations ===== | ===== Recalculations ===== | ||
Routinely, the NMVOC emissions of the last reported year must be actualized in the next reporting cycle as the final data of the foreign trade statistics are regularly only available after the publication of the respective reporting year has been completed. | Routinely, the NMVOC emissions of the last reported year must be actualized in the next reporting cycle as the final data of the foreign trade statistics are regularly only available after the publication of the respective reporting year has been completed. | ||
+ | |||
For the year 2020, this adjustment is postponed to the submission 2024 because for some applications the calculation bases also have to be reviewed for further years and this review could not be completed in time for the 2023 reporting. | For the year 2020, this adjustment is postponed to the submission 2024 because for some applications the calculation bases also have to be reviewed for further years and this review could not be completed in time for the 2023 reporting. | ||
Line 80: | Line 117: | ||
===== Planned improvements ===== | ===== Planned improvements ===== | ||
- | == Bitumen blowing | + | For bitumen blowing a visual NMVOC emission trend description will be added. |
- | The process of air blowing of bitumen could not only be conducted at oil refineries but also at asphalt processing and asphalt roofing plants. The emissions of air pollutants in that plants depend on various parameters like process conduct | + | ===== Bibliography ===== |
- | Meanwhile | + | |
+ | **Lit. 1:** UBA, 2007: Jörß, Wolfram; Handke, Volker; Lambrecht, Udo and Dünnebeil, Frank (2007): Emissionen und Maßnahmenanalyse Feinstaub 2000 – 2020. UBA-TEXTE Nr. 38/2007. Dessau-Roßlau: | ||
+ | **Lit. 2:** EMEP/EEA, 2019: EMEP/EEA air pollutant emission inventory guidebook 2019, Copenhagen, 2019 https://www.eea.europa.eu/ | ||
+ | **Lit. 3:** Official Mineral-oil Data (amtliche Mineralöldaten) of the Federal Office of Economics and Export Control (BAFA); https://www.bafa.de/ | ||
+ | **Lit. 4:** Eisele, F. (1998); Mündliche Information der Arbeitsgemeinschaft der Bitumenindustrie e.V, Persönliche Information, | ||
+ | **Lit. 5:** Theloke J., Obermeier A., Friedrich R. (Juni 2000), Ermittlung der Lösemittelemissionen 1994 in Deutschland und Methoden zur Fortschreibung. Stuttgart, Dessau-Roßlau\\ | ||
+ | **Lit. 6:** Trumbore, David C. (Owens Corning, Asphalt Technology Laboratory, Summit, IL 60501; Spring 1998). The Magnitude and Source of Air Emissions from Asphalt blowing operations. // |