2.A.5.b - Construction and Demolition

Short description

Category Code Method AD EF
2.A.5.b T1 NS CS
Key Category SO₂ NOₓ NH₃ NMVOC CO BC Pb Hg Cd Diox PAH HCB TSP PM₁₀ PM₂ ₅
2.A.5.b - - - - - - - - - - - - L/- L/T -/-

Click to view Legend

Click to hide Legend

T = key source by Trend L = key source by Level

D Default
RA Reference Approach
T1 Tier 1 / Simple Methodology *
T2 Tier 2*
T3 Tier 3 / Detailed Methodology *
CS Country Specific
M Model
* as described in the EMEP/CORINAIR Emission Inventory Guidebook - 2007, in the group specific chapters.
AD - Data Source for Activity Data
NS National Statistics
RS Regional Statistics
IS International Statistics
PS Plant Specific data
AS Associations, business organisations
Q specific questionnaires, surveys
EF - Emission Factors
D Default (EMEP Guidebook)
C Confidential
CS Country Specific
PS Plant Specific data

For particulate emissions, Construction is the second main emissions source in the Mineral industries.


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) 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.

Activity data

Activity data are determined taking into account figures for various construction activities. Data is based on production statistics (national statistics). According to the method used, figures of area of land affected by construction activities per building were concluded from statistical data and multiplied with emission factors, as explained below. The common uncertainty of 3% for national statistics could be increased as a result of this calculation, but the effect is not estimated at the moment.

Emission factors

The emission factors used are results of Adaptation of UNECE-Defaults (EEA, 2016) 2), see chapter NFR 2.A.5.b for different kind of buildings.

Table 1: Overview of apllied emission factors

Kind of building Pollutant EF value Unit EF trend
single and two family houses TSP 0.0638 kg/m²*y constant
single and two family houses PM₁₀ 0.0191 kg/m²*y constant
single and two family houses PM₂.₅ 0.0019 kg/m²*y constant
apartment buildings TSP 0.329 kg/m²*y constant
apartment buildings PM₁₀ 0.099 kg/m²*y constant
apartment buildings PM₂.₅ 0.0099 kg/m²*y constant
non-residential TSP 0.631 kg/m²*y constant
non-residential PM₁₀ 0.189 kg/m²*y constant
non-residential PM₂.₅ 0.0189 kg/m²*y constant
roads TSP 1,674 kg/m²*y constant
roads PM₁₀ 502 kg/m²*y constant
roads PM₂.₅ 50.2 kg/m²*y constant

Several further assumptions were necessary to use the formula of the Guidebook:

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 (EEA, 2016)3):

Type of building Estimated duration (year)
Construction of houses (single and two family) 0.5 (6 months)
Construction of apartments (all types) 0.75 (9 months)
Non-residential construction 0.83 (10 months)
Road construction 1 (12 months)

AD is a result of multiplying B the number of houses constructed and f the conversion factor.

All trends in emissions as product of EF and AD correspond to trends of construction activities.

Emission trends in NFR 2.A.5.b


With activity data and emission factors remaining unrevised, no recalculations have been carried out compared to last year's submission.

For pollutant-specific information on recalculated emission estimates for Base Year and 2018, please see the pollutant specific recalculation tables following chapter 8.1 - Recalculations.

Planned improvements

At the moment, no category-specific improvements are planned.


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.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.

1) Umweltbundesamt, 2016: Development of Methods for the Generation of Emission Data for Air Pollutants from Building Activity and Construction Zones, Dessau-Roßlau, 2016 FILE?
2), 3) EEA, 2016: EEA Report No 21/2016 EMEP EEA air pollutant emission inventory guidebook 2016, Copenhagen, 2016; https://www.eea.europa.eu/ds_resolveuid/EJ6RT9P2Y3