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Inventories of CO2 emissions from international shipping 2007–2012 39<br />
2 assign fleet sectors to domestic service and subtract from fleet;<br />
3 combine T-D heuristics and fleet sector information to match the vessel types most likely to serve<br />
domestic shipping (bottom-up) with expectations of total fraction likely to use domestic bunkers<br />
(top-down).<br />
The Second IMO GHG Study 2009 used method 3, a combined application of the top-down heuristic<br />
and removal of some vessel types. However, the study noted significant uncertainties with this approach.<br />
Specifically, it assumed that ship activity was proportional to data on seaborne transport. The study noted<br />
that, over the course of a year’s activity, a given vessel could be engaged in both international shipping<br />
and domestic navigation. “Since the [Second IMO GHG Study 2009] activity-based model cannot separate<br />
domestic shipping from international shipping, figures from bunker statistics for emissions from domestic<br />
shipping [were] used in the calculation of emissions from international shipping” (Second IMO GHG Study<br />
2009, paragraph 3.17). This study explicitly removed fleet sectors associated with fishing, fixed offshore<br />
installations (production vessels) and domestic navigation relying on fuel totals reported in their top-down<br />
analysis based on IEA statistics.<br />
The Third IMO GHG Study 2014 consortium chose not to apply allocation methods 1 or 3 and selected<br />
method 2, for several reasons. Method 1 requires a simplistic and arbitrary direct application of the top-down<br />
fuel ratios to bottom-up totals. The main disadvantage of method 1 is that it can be applied to the inventory<br />
total only; results cannot be tied to bottom-up insights within vessel categories. A related disadvantage is<br />
that the assumption may be untestable, preventing direct quality assurance or control and disabling any<br />
quantitative consideration of uncertainty.<br />
Allocation method 3 requires subjective judgements to be imposed on the bottom-up data beyond a testable<br />
set of assumptions applied to vessel types. For example, the 2009 study imposed additional definitions of<br />
oceangoing and coastwise shipping, designating some fleet sectors like cruise passenger ships, service and<br />
fishing vessels and smaller ro-pax vessels as coastwise. However, that study did not reconcile or discuss<br />
whether the fuel totals allocated to coastwise vessels corresponded to an international versus domestic<br />
determination within its activity-based method. Moreover, an attempt to determine which shipping was<br />
coastwise, as opposed to transiting along a coastal route, was beyond scope of the study.<br />
The Third IMO GHG Study 2014 applies allocation method 2 with information provided in AIS to support<br />
the bottom-up methodology. Based on general voyage behaviour, some ship types are likely to engage in<br />
international shipping more often than domestic navigation. These types include transport and larger ferry<br />
vessels, as listed in Table 12. This allocation, therefore, also identifies ship types that can be expected to<br />
engage mostly in domestic navigation, including non-transport vessels, such as offshore and service vessels,<br />
yachts and smaller regional ferry vessels (see Table 13). Results using allocation method 2 allow comparison<br />
between bottom-up and top-down allocation of international shipping and domestic navigation. As a caveat,<br />
method 2 might overestimate international shipping and could increase uncertainty, which is discussed in<br />
Sections 1.4 and 1.5.