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--- sector:ippu:mineral_industry:construction_demolition:start [2021/02/03 14:28] – [Short description] gniffke
+++ sector:ippu:mineral_industry:construction_demolition:start [2024/11/06 13:54] (current) – external edit 127.0.0.1
@@ Line 3: / Line 3: @@
 ===== Short description =====
-^  Method  ^  AD  ^  EF  ^  Key Category                   ^
+^  Category Code                          ^  Method  ^  AD  ^  EF  ^
-|  T1      |  NS  |  CS  |  **L&T:** TSP, PM₁₀  |
+|  2.A.5.b                                |  T1/T2   |  NS  |  CS  |
+|  {{page>general:Misc:LegendEIT:start}}                        ||||
-{{page>general:Misc:LegendEIT:start}}
+----
+|  NO<sub>x</sub>                         |  NMVOC  |  SO<sub>2</sub>  |  NH<sub>3</sub>  ^  PM<sub>2.5</sub>  ^  PM<sub>10</sub>  ^ TSP   |  BC  |  CO  |  Heavy Metals  |  POPs  |
+|  NA                                     |  NA     |  NA              |  NA              |  -/-               ^  L/T              ^  L/-  |  NA  |  NA  |  NA            |  NA    |
+|  {{page>general:Misc:LegendKCA:start}}                                                                                                                                 |||||||||||
-Information about the key source relevance can be found in [[sector:ippu:mineral_industry:start|2.A - Mineral Industry]]. For particulate emissions, Construction is the main emissions source in the Mineral industries.
+\\
+With respect to particle emissions, construction is the second main emissions source in the Mineral industries.
 ===== Methodology =====
-Since the last update of the UNECE Guidebook we use the Tier 1 method to estimate the national emissions of particulate matters. The approach for uncontrolled fugitive emissions for this source category was adapted for national circumstances within a research Project (Umweltbundesamt, 2016) [((bibcite 1))], partly considered exiting control techniques. As a result, the information of the statistics is combined with modified default emission factors for TSP and PM.
+Since the last update of the UNECE Guidebook, a Tier 1 method is applied to estimate particulate matter emissions. The T1 GB method is used by us with various adaptations to national conditions, so this is already higher tier, perhaps as T1/T2.
+The approach for uncontrolled fugitive emissions for this source category was adapted for national circumstances within a research Project (Umweltbundesamt, 2016) [(Umweltbundesamt, 2016: Development of Methods for the Generation of Emission Data for Air Pollutants from Building Activity and Construction Zones, Dessau-Roßlau, 2016, https://research.ebsco.com/linkprocessor/plink?id=46c9c9e5-c6f9-3229-b7af-6585eb409115)], partly considered exiting control techniques. As a result, the information of the statistics is combined with modified default emission factors for TSP and PM.
 ==== Activity data ====
@@ Line 21: / Line 29: @@
 ==== Emission factors ====
-The emission factors used are results of Adaptation of UNECE-Defaults (EEA, 2016) [((bibcite 2))], see chapter NFR 2.A.5.b for different kind of buildings.
+The emission factors used are results of Adaptation of UNECE-Defaults (EEA, 2016) [(EEA2023>EEA, 2023: EEA Report No 03/2023 EMEP EEA air pollutant emission inventory guidebook 2023, Copenhagen, 2023; https://www.eea.europa.eu/publications/emep-eea-guidebook-2023/part-b-sectoral-guidance-chapters/2-industrial-processes-and-product-use/2-a-mineral-products/2-a-5-b-construction/view)].
-__Table 1: Overview of apllied emission factors__
+__Table 1: Overview of apllied emission factors, in [kg / m<sup>2</sup> * y, for roads in tons / km<sup>2</sup> * y]__
-||~ kind of building				||~ pollutant 	||~ EF value 	||~ unit			||~ EF trend ||
+^ Kind of building              ^  Pollutant         ^  EF value  ^  EF trend  ^
-|| single and two family houses 	|| TSP 		||  0.0638 	|| kg/m^^2^^ * y || constant||
+| single and two-family houses  |  TSP               |  0.0638    |  constant  |
-|| single and two family houses 	|| PM,,10,, 	||  0.0191 	|| kg/m^^2^^ * y || constant||
+| :::                           |  PM<sub>10</sub>   |  0.0191    |  constant  |
-|| single and two family houses 	|| PM,,2.5,, 	||  0.0019 	|| kg/m^^2^^ * y || constant||
+| :::                           |  PM<sub>2.5</sub>  |  0.0019    |  constant  |
-|| apartment buildings			 || TSP 		||  0.329 		|| kg/m^^2^^ * y || constant||
+| apartment buildings           |  TSP               |  0.329     |  constant  |
-|| apartment buildings 			|| PM,,10,, 	||  0.099 		|| kg/m^^2^^ * y || constant||
+| :::                           |  PM<sub>10</sub>   |  0.099     |  constant  |
-|| apartment buildings 			|| PM,,2.5,, 	||  0.0099 	|| kg/m^^2^^ * y || constant||
+| :::                           |  PM<sub>2.5</sub>  |  0.0099    |  constant  |
-|| non-residential 				|| TSP 		||  0.631		 || kg/m^^2^^ * y || constant||
+| non-residential               |  TSP               |  0.631     |  constant  |
-|| non-residential 				|| PM,,10,, 	||  0.189 		|| kg/m^^2^^ * y || constant||
+| :::                           |  PM<sub>10</sub>   |  0.189     |  constant  |
-|| non-residential 				|| PM,,2.5,, 	||  0.0189 	|| kg/m^^2^^ * y || constant||
+| :::                           |  PM<sub>2.5</sub>  |  0.0189    |  constant  |
-|| roads 						|| TSP 		||  1,674 		|| t/km^^2^^ * y || constant||
+| roads                         |  TSP               |  1,674     |  constant  |
-|| roads 						|| PM,,10,, 	||  502 		|| t/km^^2^^ * y || constant||
+| :::                           |  PM<sub>10</sub>   |  502       |  constant  |
-|| roads 						|| PM,,2.5,, 	||  50.2 		|| t/km^^2^^ * y || constant||
+| :::                           |  PM<sub>2.5</sub>  |  50.2      |  constant  |
 Several further assumptions were necessary to use the formula of the Guidebook:
-||~ EM=EF*B*f*m||
+| EM = EF * B * f * m     ||
-The EF is adapted with Moisture Level Correction factor and Silt Content Correction factor in all cases, both 0.20 and 2.22. The assumption about the duration of the construction activity uses the Default values.
+The EF is adapted with Moisture Level Correction factor and Silt Content Correction factor in all cases, both 0.20 and 2.22. The assumption about the duration of the construction activity uses the Default values (EEA, 2023)[(EEA2023)]:
-||~ Type of building ||~ Estimated duration (year) ||
+^ Type of building                                   ^^  Estimated duration (year)      ^^
-|| Construction of houses (single and two family) || 0.5 (6 months) ||
+| Construction of houses (single and two family)     ||  0.5 (6 months)                 ||
-|| Construction of apartments (all types) || 0.75 (9 months) ||
+| Construction of apartments (all types)             ||  0.75 (9 months)                ||
-|| Non-residential construction || 0.83 (10 months) ||
+| Non-residential construction                       ||  0.83 (10 months)               ||
-|| Road construction || 1 (12 months) ||
+| Road construction                                  ||  1 (12 months)                  ||
-Source (EEA, 2016) [((bibcite 2))]
 AD is a result of multiplying B the number of houses constructed and f the conversion factor.
-+ __Trends in emissions__
+===== Trends in emissions =====
 All trends in emissions as product of EF and AD correspond to trends of construction activities.
-[[gallery size="medium" viewer="yes"]]
+[{{:sector:ippu:mineral_industry:EM_2A5b_since_1990.PNG|**Emission trends in NFR 2.A.5.b**}}]
-: EM_2A5b_since_1990.PNG
-[[/gallery]]
-+ __Recalculations__
+Notes to PCB emissions of old buildings are given in chapter [[sector:ippu:pops_and_hm_consumption:start|2.K - Consumption of POPs and Heavy Metals]].
-With **activity data** and **emission factors** remaining unrevised, no recalculations have been carried out compared to last year's submission.
+===== Recalculations =====
-<WRAP center round info 60%>
+<WRAP center round info 65%>
-For pollutant-specific information on recalculated emission estimates for Base Year and 2018, please see the pollutant specific recalculation tables following [[general:recalculations:start|chapter 8.1 - Recalculations]].
+With **all input data remaining unrevised**, no recalculations were made compared to the previous submission.
 </WRAP>
-=====Planned improvements =====
+=====Planned improvements =====
 At the moment, no category-specific improvements are planned.
 ===== FAQs =====
+//**Where can I find emissions estimation of demolition activities?**// - Demolishing without any significant new construction is not covered and there are no other emission factors available for demolition activities only. Nevertheless you can find Information about emissions from
-//**Where can I find emissions estimation of demolition activities?**// - Demolishing without any significant new construction is not covered and there are no other emission factors available for demolition activities only. Nevertheless you can find Information about emissions from [[[5-e-buildings-cars-fires | buildings fires]]].
+[[sector:waste:other_waste:building_and_car_fires:start|5.E.2 - Other Waste: Building Fires]].
 //**Why do German EFs differ from EEA defaults?**// - It has to do with the default 50% reduction for non-residential buildings and roads (as a result of wetting unpaved temporary roads) that is assumed in the calculations for Germany. This is also already accounted for in the EPA emission factors. It is a result of a control measure that is nearly always taken but in principle optional. In the Guidebook a 50% reduction is advised.
-------
-[[bibliography]]
-: 1 : Umweltbundesamt, 2016: Development of Methods for the Generation of Emission Data for Air Pollutants from Building Activity and Construction Zones, Dessau-Roßlau, 2016;
-[!--URL: http://webde/gruppen/bibliothek/OnlineReports/EF000592.pdf--]
-[[file project-report_evaluation_CONSTRUCTION.pdf | Document (PDF)]]
-: 2 : EEA, 2016: EEA Report No 21/2016 EMEP EEA air pollutant emission inventory guidebook 2016, Copenhagen, 2016;
-URL: https://www.eea.europa.eu/ds_resolveuid/EJ6RT9P2Y3
-[[/bibliography]]

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