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Third IMO Greenhouse Gas Study 2014

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178 <strong>Third</strong> <strong>IMO</strong> GHG <strong>Study</strong> <strong>2014</strong><br />

sfc = sfc e × f e eq. (3)<br />

The assumptions for sfc e are described in detail in Section 2 and the associated Annex 6. f e is estimated from<br />

manufacturers’ data, as described in Section 2.<br />

Aggregation by ship type and size<br />

As discussed in Section 1.2, the activity and fleet data merger matches the IHSF fleet data to the AIS data,<br />

determining whether there is a match by ship and whether the activity data is of good or poor quality. Good<br />

quality activity data is currently defined as having day coverage of 10% or greater, although this assumption<br />

will be tested for its impact on quality and uncertainty in Sections 1.4 and 1.5. The matched data is filtered for<br />

good quality, creating a per-ship profile. The values in the per-ship profile are averaged across ship type and<br />

size bins to create an aggregate ship type profile.<br />

Fleet estimate assembly<br />

Further estimation is required for unmatched ships within both a ship type and size category. The aggregate<br />

average ship type and size profile is used to estimate the speed and draught profile, and this is then deployed<br />

with the ship’s technical specification to calculate fuel use and emissions. This assumes that the mean speed<br />

and draught for the ship type and size bin is representative of all ships within that type and size bin. Once this<br />

step is completed, the per-ship profile is merged with the backfilled ships and the same aggregation by ship<br />

type and size bin category is performed, this time with the complete fleet of in-service ships. The effect of the<br />

uncertainty in the operational profile of the unmatched ships on the total inventory emissions is considered<br />

further in the uncertainty analysis.

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