2.G(c) - Use of Charcoal for barbecues

Category Code Name of Category Method AD EF
2.G© Other Product use: Fireworks T1 NS C

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Method(s) applied
D Default
T1 Tier 1 / Simple Methodology *
T2 Tier 2*
T3 Tier 3 / Detailed Methodology *
C CORINAIR
CS Country Specific
M Model
* as described in the EMEP/EEA Emission Inventory Guidebook - 2019, in category chapters.
(source for) Activity Data
NS National Statistics
RS Regional Statistics
IS International Statistics
PS Plant Specific
As Associations, business organisations
Q specific Questionnaires (or surveys)
M Model / Modelled
C Confidential
(source for) Emission Factors
D Default (EMEP Guidebook)
CS Country Specific
PS Plant Specific
M Model / Modelled
C Confidential


In this sub-category of 2.G - Other product use, Germany reports the following emissions resulting from the burning of charcoal for barbecues:

NOx NMVOC SO2 NH3 PM2.5 PM10 TSP BC CO Heavy Metals POPs
NE NE NE NE -/- -/- -/- NE NE NE NE

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L/- key source by Level only
-/T key source by Trend only
L/T key source by both Level and Trend
-/- no key source for this pollutant
IE emission of specific pollutant Included Elsewhere (i.e. in another category)
NE emission of specific pollutant Not Estimated (yet)
NA specific pollutant not emitted from this source or activity = Not Applicable
* no analysis done


Method

The amount of charcoal used for barbecue has been ever-expanding from 1990 to 2012 and is predominantly imported.

After several years with stable demand, consumption is declining the fourth consecutive year.

However, as there is only one big producer, used amounts and emission factors are considered confidential and cannto be provided here.

Activity data

The annual charcoal consumption for barbecue is calculated as

annual imports + annual domestic production - annual exports

,

with the relevant amounts of charcoal derived from national statistics provided by the Federal Statistical Office (DESTATIS).

Other applications for charcoal are not included.

The model is based on the two assumptions that (i) there is no storage of charcoal and that (ii) all charcoal is burned during usage.

Emission factors

The emission factors are comparable as those from the CEPMEIP Database (SNAP: 060508) (CEPMEIP, 2018) 1).

Uncertainties

The uncertainties of consumption are 20% and the uncertainties of emission are not more than 54% for the lower and upper bounds.

Recalculations

The import and export data for 2022 were changed as revised activity data for the foreign sale was available from the Federal Statistical Office. The emissions of PM2.5, PM10 and TSP reported for 2022 increased by 4.9 %.

For pollutant-specific information on recalculated emission estimates for Base Year and 2022, please see the pollutant specific recalculation tables following chapter 8.1 - Recalculations.

Planned improvements

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


1) CEPMEIP (2018): Co-ordinated European Programme on Particulate Matter Emission Inventories, Projections and Guidance (CEPMEIP), CEPMEIP Database, SNAP code : 060508; http://www.air.sk/tno/cepmeip/em_factors.php?PHPSESSID=cc235582eb4e09bf725d6f859deb382d