A. Sirois et Jw. Bottenheim, USE OF BACKWARD TRAJECTORIES TO INTERPRET THE 5-YEAR RECORD OF PAN AND O-3 AMBIENT AIR CONCENTRATIONS AT KEJIMKUJIK NATIONAL-PARK, NOVA-SCOTIA, JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 100(D2), 1995, pp. 2867-2881
Air parcel trajectory data are used in two ways to elucidate the tempo
ral trend analysis of 5 years of peroxyacetyl nitrate (PAN) and O-3 Ob
servations at a rural site in eastern Canada. In the first method, ''p
robability of residence'' contours are constructed to determine the mo
st probable origin of air parcels containing the highest and lowest 10
% of PAN and O-3 mixing ratios. High PAN is found to emanate always fr
om areas of high anthropogenic activity, except when the transport pat
h is to a large extent over the ocean, especially in the summer. High
O-3 originates from the same regions except in the winter when because
of low photochemical activity, O-3 is actually titrated and air from
less populated areas is richer in O-3. The trajectories indicate that
transport at higher altitude leads to higher mixing ratios; this is es
pecially the case for O-3 in winter and spring. The complementary meth
od of clustering the trajectories has allowed qualitative derivation o
f seasonal cycles for background and polluted air masses of different
origin. Background air from the north shows a distinct PAN maximum in
March; it is discussed that this could be either due to enhanced photo
chemistry or to the import of polluted air from the Arctic. Polluted a
ir masses show the same March peak, but a second peak in late summer/e
arly fall. Oceanic air from the south has a January maximum in PAN but
otherwise is consistently low in PAN. O-3 also has a spring maximum,
but in polluted air it is broader stretching into the summer. It is po
stulated that this is due to additional O-3 formation in the summer, w
hile in the winter, actual O-3 loss is indicated for polluted air. By
inference it is deduced that the second PAN peak in polluted air is al
so due to additional formation in comparison with background air, whil
e in the summer, extra PAN loss mechanisms operate that are less impor
tant for O-3. Indications for both dry deposition and thermal decompos
ition have been found.