Third IMO Greenhouse Gas Study 2014
GHG3%20Executive%20Summary%20and%20Report
GHG3%20Executive%20Summary%20and%20Report
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106 <strong>Third</strong> <strong>IMO</strong> GHG <strong>Study</strong> <strong>2014</strong><br />
This study used the following SO x EF baseline factors, based on HFO with 2.7% sulphur content. The EF baseline<br />
factors for SO x are presented in Table 42. It should be noted that SO x and SO 2 are basically interchangeable<br />
for marine-related engine emissions.<br />
Table 42 – SO x baseline emissions factors<br />
Eng speed/type Fuel 1 type ME EF baseline (kg/tonne fuel) Aux eng EF baseline (kg/tonne fuel) Reference<br />
SSD<br />
MSD<br />
HSD<br />
HFO<br />
HFO<br />
HFO<br />
52.77<br />
52.79<br />
na<br />
na<br />
52.78<br />
52.78<br />
Mass balance 2<br />
Mass balance 2<br />
Mass balance 2<br />
Otto LNG 0.02 0.02 Kunz & Gorse, 2013<br />
GT HFO 52.79 na Mass balance 2<br />
STM HFO 52.79 na Mass balance 2<br />
Notes: 1 assumes HFO fuel with 2.7% sulphur content<br />
2<br />
assumes 97.54% of sulphur fraction is converted to SO x ; remainder is converted to PM SO 4<br />
These baseline emissions factors are adjusted using FCF to account for the changing annual fuel sulphur<br />
content world averages (2007–2012) or as required regionally within an ECA. The global sulphur content<br />
of marine fuel oils was modelled according to <strong>IMO</strong> global sulphur fuel oil monitoring reports, as presented<br />
in Table 43. For regional variations driven by regulation (ECAs), the fuel sulphur content is assumed to be<br />
equivalent to the minimum regulatory requirement (see the description in Section 1.2 on how the shipping<br />
activity is attributed to different global regions). Further regional variations of fuel sulphur content were not<br />
taken into account owing to the complexity associated with points of purchase of fuel and where and when it<br />
is actually burned. It is assumed that the world average is representative across the world fleet for each year.<br />
Table 43 – Annual fuel oil sulphur worldwide averages<br />
Fuel type 2007 2008 2009 2010 2011 2012<br />
HFO/IFO 2.42 2.37 2.6 2.61 2.65 2.51<br />
MDO/MGO 0.15 0.15 0.15 0.15 0.14 0.14<br />
For further information on specific emissions factors, FCFs and references, see Annex 6.<br />
PM baseline<br />
The current literature contains a rather large variation of PM emissions factors, which vary significantly<br />
between studies because of differences in methodology, sampling and analysis techniques. The United States<br />
Environmental Protection Agency (EPA) and the California Air Resources Board (CARB) evaluated the available<br />
PM test data and determined that along with direct PM there is secondary PM associated with the sulphur<br />
in fuel (2.46% fuel sulphur fraction is converted to secondary PM while the remainder is emitted as SO x ,<br />
as discussed previously). This study used the following PM EF baseline factors based on 2.7% sulphur content<br />
HFO. The EF baseline factors for PM are presented in Table 44. It should be noted there is virtually no difference<br />
between total PM and PM less than 10 microns or PM 10 for diesel-based fuels.<br />
Table 44 – PM baseline emissions factors<br />
Eng speed/type Fuel 1 type ME EF baseline (kg/tonne fuel) Aux eng EF baseline (kg/tonne fuel) Reference<br />
SSD<br />
MSD<br />
HSD<br />
HFO<br />
HFO<br />
HFO<br />
7.28<br />
6.65<br />
na<br />
na<br />
6.34<br />
6.34<br />
EPA, 2007<br />
EPA, 2007<br />
EPA, 2007<br />
Otto LNG 0.18 0.18 Kristensen, 2012<br />
GT HFO 0.20 na IVL, 2004<br />
STM HFO 3.05 na IVL, 2004<br />
Notes: 1 assumes HFO fuel with 2.7% sulphur content