ID |
Source |
Substance |
Method |
Emission factor |
Remarks |
Projection assumptions |
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EMISSION OF
SUBSTITUTES FOR
OZONE-DEPLETING
SUBSTANCES (ODS
SUBSTITUTES) |
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Refrigerant |
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K1 |
Household fridges and freezers |
HFC-134a |
Tier 2 top-down approach:
- information on refrigerant consumption provided by reports from the main producers
of household fridges and freezers in DK, accounting for no less than an estimated
95% of the market.
Tier 2 bottom-up approach:
- information on imports and exports of refrigerants in products based on the
average quantity contained per unit and Danish statistics. |
2% release on filling (IPCC default)
1% release from stock per year (IPCC default)
Lifetime = 15 years (IPCC default)
0% release upon disposal (DK default). Up to and including 2000, the quantity
remaining upon disposal was included as emissions (IPCC default). Legislation
in Denmark ensures drawing-off of refrigerant, and consequently, the IPCC default
is misleading in the Danish context. |
Stock determined in 1998 for the period 1990-1998 based on information from
Danish producers and estimates based on import/export statistics and average quantity
of HFC contained in refrigerant and foam per unit /2/.
For the updating of stock, import/export data from 1998 is used, as well as information
on annual HFC consumption by Danish producers.1998 import/export data are equal
to net exports of 141 tonnes HFC-134a refrigerant and net exports of 1.6 tonnes
of HFC-134a in foam (note: Denmark's largest exporter does not use HFC in foam
production. Therefore, exports of HFC in foam are less than exports of refrigerants). |
From 2001, net exports of refrigerants in household fridges are assumed to
account for 50 per cent of consumption.
The consumption in the projection is not influenced by new phasing-out regulations.
The effect of charges on HFCs is expected to give an annual reduction in consumption
of 5 per cent in the period 2001-2005. |
K2 |
Commercial stationary refrigerators in retail stores, industry, etc., and
stationary A/C systems in buildings etc. |
HFC-134a, HFC-404a, HFC-401a, HFC-402a, HFC-407c, HFC-507a, other HFCs, PFCs
(C3F8) |
Tier 2 top-down approach:
- information on refrigerant consumption was provided by importers/suppliers of
refrigerants for commercial refrigerators in DK.
- information on distribution of refrigerant consumption at different sites is
estimated using information from user enterprises, the KMO and estimates from
suppliers. |
1.5% on refilling (DK default)
10% release from operation and accidents (DK default).
0% release from destruction (DK default)
In the case of re-use it is assumed release occurs during the cleaning process
equivalent to 2%. It is good practice not to account for any re-use since
the original is accounted for in sales and imports. |
In 2001/2002 an assessment was made of the national Danish leakage rate from
commercial plants. This assessment was carried out by COWI for the Danish EPA.
This result has led to a decrease in the leakage rates for filling, operation
and disposal in compliance with IPCC guidelines /16/. |
From 2007, the consumption of refrigerants merely represents the amount used
for refilling existing systems (stock). It is assumed that the consumption of
refrigerants for refilling stock will be reduced by 15 per cent in 2007 and will
then diminish by 5 per cent per year until 2014. From 2015, it is assumed that
consumption will only represent 10 per cent per year compared to current levels. |
K3 |
Refrigerated vans and lorries |
HFC-134a, HFC-404a |
Top-down Tier 2 approach
- information on refrigerant consumption in refrigerated vans and lorries is based
on consumption information from manufacturers of refrigerated vans and lorries
as well as data from the KMO. |
0.5% on refilling (DK default)
17% from operation annually (DK default, same as IPCC)
2% in reuse (DK default)
Lifetime 6-8 years
0% upon destruction; all refrigerants are drawn off and are either recycled or
destroyed at the Kommune Kemi plant |
In 2001/2002 an assessment was made of the national Danish leakage rate from
refrigerated vans and lorries. This assessment was carried out by COWI for the
Danish EPA. This result has led to a decrease in the leakage rates for filling
and disposal in compliance with IPCC guidelines. The leakage rate for operation
is still 17% in compliance with IPCC guidelines /16/. |
The tax effect has not been included, since refrigerated vans and lorries
are exempt from taxes.
Stock is defined as 7.7 tonnes (HFC-134a) and 23.2 tonnes HFC-404a in 2000 /16/.
Consumption has been projected as steady state compared to 2001. |
K4 |
Mobile A/C systems |
HFC-134a |
Tier 2 bottom-up and top-down approach. Bottom-up approach for definition
of Danish emission factor and estimate for stock and imports. Top-down approach
used for gathering of consumption data from importers for refilling of mobile
A/C systems. |
0.5% on refilling (DK default)
33% annual release during operation (complete refilling every 3 years - DK default).
Lifetime for mobile A/C systems that are serviced is 6 years, equivalent to two
refillings. Systems do not undergo maintenance after 6 years (DK default).
0% loss at destruction. Gas is collected and re-used/cleaned, or treated at Kommune
Kemi (DK default).
Emissions are calculated as 1/3 of stock from the previous year (n-1). This means
the stock is the central calculation parameter. The stock is calculated using
DAF annual statistics in relation to a number of conditions defined in /16/. Consumption
per annum gives the quantity used in refilling systems which undergo servicing
(max. 50% of existing systems). |
In 2001/2002 an assessment was made of the national Danish leakage rate from
mobile A/C systems. This assessment was carried out by COWI for the Danish EPA.
This result has led to a small increase in the leakage rate for operation and
a decrease for filling and disposal in compliance with IPCC guidelines /16/.
The stock figures are updated using statistics on vehicles in Denmark from DAF.
The average expected filling for cars and vans is 750 g, 1.2 kg for lorries under
6 tonnes, 1.5 kg for lorries over 6 tonnes, and 9 kg for buses. Further calculation
assumptions appear from /16/. |
The projection is based on a steady state stock (203 tonnes). |
|
Foam production |
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S1 |
Foam in household fridges and freezers (closed cell) |
HFC-134a |
Tier 2 top-down + bottom-up approach:
- information on foam blowing agent consumption provided by reports from the main
producers of household fridges and freezers in DK, accounting for no less than
an estimated 95% of the market. |
10% release in foam production (IPCC default)
4.5% release from stock per year (IPCC default)
Lifetime = 15 years (DK default)
22.5% remaining upon disposal which is destroyed in incineration and thereby is
not released as emissions (DK default). |
Stock of HFC in foam determined in 1998 for the period 1990-1998 based on
information from Danish producers and estimates based on import/export statistics
and average quantity of HFC contained in refrigerant and foam per unit /2/.
For the updating of stock, import/export data from 1998 is used, as well as information
on annual HFC consumption by Danish producers. 1998 import/export data are equal
to net exports of 141 tonnes HFC-134a refrigerant and net exports of 1.6 tonnes
of HFC-134a in foam (note: Denmark's largest exporter does not use HFC in foam.
Therefore, exports of HFC in foam are less than exports of refrigerants). |
|
S2 |
Soft foam (open cell) |
HFC-134a
HFC-152a
Other HFCs (HFC-365) |
Tier 2
- information on foam blowing agents for soft foam is derived from reports provided
by the main producer in Denmark, which still employs HFC in foaming processes.
This producer is thought to represent approx. 80% of the Danish soft foam consumption. |
Emissions = 100% of the HFCs sold in the current year (IPCC default) |
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S3 |
Joint filler (open cell) |
HFC-134a
HFC-152a |
Tier 2 top-down approach.
There are no longer any Danish producers of joint filler employing HFC as a foaming
agent. Emissions are due to previous estimates by producers of imported joint
filler products. |
Emissions = 100% of imported quantity contained in joint filler in the current
year (IPCC default). |
The estimated imports in 1998 by a joint filler producer were 10 tonnes HFC-134a
and 1 tonne HFC-152a.
This estimate was based on the assumption that there is an average of 100 g HFC-134a
and 25 g HFC-152a per tin of joint filler imported. |
|
|
Foaming of polyether (for shoe soles) |
HFC-134a
HFC-152a |
Tier 2 top-down approach
Information regarding consumption is identical to the consumption reported by
producer in 1999 + an estimate of imports/exports of HFC in shoe soles, 1998.
Tier 2 bottom-up approach:
Imports of HFCs contained in shoes are based on the average amount per shoe and
on Danish statistics. |
Emissions (Danish default):
- Production = 15%
- Use = 4.5%
- Lifetime = 3 years
- Disposal = 71.5%, destroyed in incineration and thereby is not released as emissions. |
The calculation of the HFC stock in shoe soles is based on the following assumptions:
it is assumed that 5% of all shoes with plastic, rubber and leather soles contain
polyether holding 8 g of HFC-134a per shoe.
Net exports with the same consumption in Danish production are 0.3 tonnes HFC-134a. |
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Aerosols |
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Aerosol sprays (industrial products) |
HFC-134a |
Tier 2.
- information on propellant consumption is derived from reports on consumption
from the only major producers of HFC-containing aerosol sprays in Denmark. The
importers are estimated to account for 100% of Danish consumption. |
Emissions = 50% of the HFC sold to this area of application in the current
year and 50% of the consumption in the second year (IPCC default for top-down
data) |
Top-down data.
Estimates of imports/exports are based on the producer's assessment of imports
equivalent to 20% of Danish production in the current year. Exports are quantified
by the producer. |
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MDI (metered dose inhalers) |
HFC-134a |
Tier 2 bottom-up approach
- consumption was studied in 1999 and was evaluated as minimal. |
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Due to minimal emissions, this class of products is no longer included in
Denmark's national inventory. |
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Solvents |
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R1 |
Liquid cleaners |
PFC (C3F8 Perfluoro-propane) |
Tier 2
- information on consumption of PFC in liquid cleaners is derived from two importers'
sales reports. This is thought to represent 100% of the Danish consumption of
PFCs in liquid cleaners. |
Emissions = 50% of the HFC sold to this area of application in the current
year and 50% of the consumption in the second year (IPCC good practice for top-down
data) |
|
Top-down data
Being phased out, cf. Statutory Order of 1/9 2002. It is assumed that the consumption
is equally distributed over all months. |
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EMISSIONS OF SF6
FROM ELECTRICAL
EQUIPMENT AND
OTHER SOURCES |
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Insulating gas in double glazing |
SF6 |
Tier 2
- information on consumption of SF6 in double glazing is derived from
importers' sales reports to the application area. The importers account for 100%
of the Danish sales of SF6 for double glazing. In addition, the largest
producer of windows in Denmark has provided consumption data, with which import
information is compared. |
Emissions (DK default):
- 15% during production of double glazing.
- 1% per year during the lifetime of the double glazing.
- Lifetime = 20 years
- Disposal - 66% of the filled content of double glazing in the production year.
- Net exports = 50% of the consumption in the current year |
|
Emissions data and lifetimes are based on information from the window producers
and industry experts in Denmark /2/.
The stock is determined on the basis of consumption information provided by importers
back to 1990. The first Danish consumption was registered in 1991.
In the projection of emissions, it is assumed that the consumption of SF6
in Danish window production will be phased out by 2003, after which emissions
will arise from stock only. |
|
Insulating gas in high-voltage power switches |
SF6 |
Tier 3c country-level mass-balance approach
- information on consumption of SF6 in high-voltage power switches
is derived from importers' sales reports (gas or gas-containing products). The
importers account for 100% of the Danish sales of SF6.
The electricity sector also provides information on the installation of new plant
and thus whether the stock is increased. |
Emissions (DK default):
- release on filling = 5%
- release during operation = 0.5% per year
- release in reuse/drawing off = 5%.
- release upon disposal = 0% |
|
There is one supplier (Siemens) that imports its own gas for filling in Denmark.
Suppliers (AAB, Siemens, Alstom) report on new installations.
The stock in 2000 was 57.6 tonnes of SF6 , which covers power switches
of all sizes in production and transmission plants. The stock has been evaluated
on the basis of a questionnaire survey in 1999 which encompassed the entire Danish
electricity sector /11/. |
|
Shock-absorbing gas in Nike Air training footwear |
SF6 |
Tier 2 top-down approach
Importer has estimated imports to Denmark of SF6 in training footwear. |
Lifetime training footwear = 5 years |
|
Importer/wholesaler reports that imports for the period 1990-1998 amounted
to approx. 1 tonne, equivalent to emissions of 0.11 tonnes per year in the period
1995-2003. For the period 1999-2005, the importer estimated imports to represent
approx. 1/3, corresponding to 0.037 tonnes per year in the period 2004-2010. |