GHG emissions from O&G operations
Friday, October 28, 2011
European Union on track to meet Kyoto commitments
Friday, June 24, 2011
What is going on with GHG emissions reporting in the Oil & Gas sector?
Thursday, September 30, 2010
WCI and reporting in Canada
The objective of one-window reporting in Canada implies that the data will be submitted to Environment Canada once and the reports distributed from there to other jurisdictions, this has been the mandate from the Canadian Council of Ministers; a similar development is expected in US where the reporting window will be EPA.
It was clarified that for BC regulations, the deadline for the 2010 emissions report is March 31 2011 for all facilities at 25,000 tonnes and above. Further technical details were addressed in the Q&A session including:
- Portable equipment in use in oil & gas such as emergency generators and portable flares will be excluded
- Stationary combustion sources over 250 MMBTU/hr heat input must measure carbon content of fuel or install CEMS (continuous emissions monitoring systems)
- Some emission factors were published with errors and have been fixed
- When using natural gas of a specified HHV range, emission factors are acceptable
- There will be flexibility in methods for process vents
A new conference call will be announced to deal specifically with oil & gas reporting, it is expected that EPA will also publish a final version of Subpart W for this sector in the near future.
Friday, July 30, 2010
Emission Factors in Oil Refineries
The most efficient approach to estimate GHG emissions from a number of Oil & Gas facilities relies on the use of generic emission factors that are usually tied with production volumes. Recently a representative from Petrobras presented some interesting information about their approach to GHG emissions inventories. The main sources for emission factors they have used are EPA- AP42 and ARPEL.
AP-42, Compilation of Air Pollutant Emission Factors, has been published since 1972 as the primary compilation of EPA's emission factor information. EPA has published supplements and updates to the fifteen chapters available in Volume I, Stationary Point and Area Sources. (see http://www.epa.gov/ttnchie1/ap42/)
ARPEL (REGIONAL ASSOCIATION OF OIL AND NATURAL GAS COMPANIES IN LATIN AMERICA AND THE CARRIBBEAN) has also published some emission factors that are more closely representative of conditions in the region.
The main conclusions from the comparisons made by Petrobras are that ARPEL’s factors tend to overestimate emissions by some 4x although these factors are specifically for oil refineries. A few other considerations and differences between emission factor sources refer to basic assumptions in their development; for instance it was noted that AP42 does not consider air preheating effects in their prediction of NOx (the effect here is that at higher temperatures thermal efficiency improves but NOx formation increases as well).
AP42 trends were to underestimate 2-3X emissions for individual sources. A drawback from these systems is that they have been calculated based on “typical” fuels and do not apply well for refinery off gases. Overall however the authors noted that the deviations introduced by these emission factors tended to cancel each other and that, for a site with a large number of sources, the final inventory would be fairly accurate.