Abstract. Conventional passive air samplers (PAS) and passive dry deposition
samplers (PAS-DD) were deployed along a 90 km south–north transect at five sites in
the Athabasca oil sands region (AOSR) during October to November 2015. The purpose
was to compare and characterize the performance of the two passive sampling
methods for targeted compounds across a range of site types. Samples were
analyzed for polycyclic aromatic compounds (PACs), nitrated polycyclic
aromatic hydrocarbons (NPAHs), and oxygenated PAHs (OPAHs). ΣPAC and
ΣNPAH concentrations were highest in PAS and PAS-DD samplers at site
AMS5, which is the closest sampling site to surface mining and upgrading
facilities. The OPAHs were elevated at site AMS6, which is located in the
town of Fort McMurray, approximately 30 km south of the main mining area.
PAS-DD was enriched relative to PAS in particle-associated target
chemicals, which is consistent with the relatively more open design of
PAS-DD intended to capture particle-phase (and gas-phase) deposition. Petroleum
coke (petcoke) (i.e., the carbonaceous byproduct of bitumen upgrading) and
oil sands ore (i.e., the material mined in open-pit mines from which bitumen
is extracted) were assessed for their potential to be a source of PACs to
air in the oil sands region. The ore samples contained ∼ 8
times and ∼ 40 times higher ΣPACs concentrations (dry
weight basis) than delayed and fluid petcoke, respectively. The residue
analysis of ore and petcoke samples also revealed that the chemical
4-nitrobiphenyl (4-NBP) can be used to track gas-phase emissions to air. A
comparison of chemical residues in ore, petcoke, and air samples revealed
that the ore is likely a major contributor to volatile PACs present in air
and that both ore and petcoke are contributing to the particle-associated
PACs in air near open-pit mining areas. The contribution of petcoke
particles in passive air samples was also confirmed qualitatively using
scanning electron microscopy coupled with energy dispersive X-ray
spectroscopy (SEM-EDS).