8.3 Reductions in Indirect Emissions
In contrast to Scope 1 emissions, which are direct GHG emissions
(i.e., GHG emissions from what the Corporate Standard’s glossary describes as
“sources that are owned or controlled by the reporting company”), Scope 2 and Scope
3 emissions are indirect GHG emissions (i.e., GHG emissions that, as described in
the Corporate Standard’s glossary, “are a consequence of the operations of the
reporting company, but occur at sources owned or controlled by another company”).
Therefore, reductions in Scope 2 and Scope 3 emissions are more difficult to
calculate accurately than reductions in Scope 1 emissions. Because indirect GHG
emissions often incorporate many factors, any reductions in these emissions are not
necessarily a direct result of the reporting company. That is, it may be difficult
to correlate reductions in Scope 2 or Scope 3 emissions with projects or initiatives
the reporting company executed. As discussed in Section 6.3, both activity data and emission
factors are used to calculate GHG emissions resulting from Scope 3 activities. Since
emission factors increase or decrease over time depending on a number of factors
unrelated to the reporting company, it can be challenging for the reporting company
to accurately present GHG emission reductions resulting from its own activities.
For example, Scope 3, Category 4 (upstream transportation and
distribution), includes GHG emissions from transportation and distribution
activities such as air transport, rail transport, road transport, and marine
transport. As discussed in Section
6.3, the Scope 3 Standard divides Scope 3 emissions into upstream GHG
emissions (i.e., indirect emissions related to purchased goods or services) and
downstream GHG emissions (i.e., indirect emissions related to sold goods or
services). Specifically, Category 4 includes both inbound and outbound
transportation services provided by third parties if paid for by the reporting
company. There are multiple methods for calculating these emissions (i.e.,
fuel-based, distance-based, or spend-based). Under the fuel-based method, the
reporting company would apply an appropriate emission factor for the type of fuel
used as determined and regulated by the EPA, which is based on numerous factors not
directly attributable to the reporting company. Therefore, when changes in GHG
emissions over time relative to a base year result in reductions, the reductions may
not be solely attributable to the reporting company’s activities.
Companies are encouraged to keep the following in mind when reporting reductions in
indirect GHG emissions:
Corporate Standard, Chapter 8, “Accounting for GHG
Reductions,” Pages 59–60
Generally, as long as the accounting of indirect emissions
over time recognizes activities that in aggregate change
global emissions, any such concerns over accuracy should not
inhibit companies from reporting their indirect emissions.
In cases where accuracy is more important, it may be
appropriate to undertake a more detailed assessment of the
actual reduction using a project quantification
methodology.
The excerpt above indicates that when accuracy is more important to stakeholders, it
is advisable for reporting companies to consider whether calculations performed
under project accounting would more appropriately reflect the reductions.
Improvements to accuracy could include obtaining more accurate sources of data or
using more specific methods of calculating GHG reductions. For example, a reporting
company may rely on secondary data (i.e., industry averages) when calculating
reductions. However, the need to obtain primary data (i.e., data obtained directly
from suppliers or other value chain partners) warrants consideration when accuracy
is more important to the reporting company’s reporting and disclosures.