2010 Progress Report - International Joint Commission
2010 Progress Report - International Joint Commission
2010 Progress Report - International Joint Commission
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<strong>Progress</strong> <strong>Report</strong> <strong>2010</strong><br />
Critical Loads and Exceedances<br />
A region’s critical load is the amount of<br />
acid deposition it can tolerate without<br />
being adversely affected according to<br />
present knowledge. When fi rst utilized in<br />
Canada, 6 the critical load was expressed<br />
in terms of sulphate deposition only and reported as<br />
kg/ha/yr. In order to simultaneously account for both<br />
sulphur (S) and nitrogen (N) acidifying inputs (S and<br />
N have different atomic weights), the critical load is<br />
currently expressed in terms of charge equivalents as<br />
eq/ha/yr. The 20 kg/ha/yr wet sulphate target load that<br />
was used to guide implementation of a SO 2<br />
emission<br />
reduction program in eastern Canada during the 1980s<br />
equals 416 eq/ha/yr.<br />
CANADA<br />
In the 1980s and 1990s, management of the emissions<br />
that produce acid deposition in Canada focused on the<br />
east where sensitive terrain was coincident with high<br />
levels of deposition. Limited survey and monitoring<br />
data supported an assumption that acid deposition was<br />
not a problem in western Canada. This was in keeping<br />
with the fact that western sources were generally<br />
distant from sensitive terrain. However, expansion of<br />
existing and development of new emission sources<br />
in western Canada required that this assumption be<br />
re-evaluated. Recent regional surveys of lakes located<br />
on the Canadian Shield conducted by federal and<br />
provincial authorities 7 have allowed determination of<br />
representative aquatic critical loads for northern parts<br />
of Manitoba and Saskatchewan. Steady-state critical<br />
loads were calculated on a lake-by-lake basis using<br />
the Steady-State Water Chemistry (SSWC) model and<br />
an acid neutralizing capacity threshold (ANC limit<br />
) that<br />
considered the infl uence of the high level of dissolved<br />
organic carbon (DOC) which is prevalent throughout<br />
the region. The critical load for a regional data set was<br />
estimated by the 5 th percentile value so as to protect<br />
95% of the lake ecosystems. Regional aquatic critical<br />
loads ranged from 1.9 to 52.7 eq/ha/yr indicating that<br />
very acid-sensitive lakes exist throughout northern<br />
Manitoba and Saskatchewan. The lowest regional<br />
critical loads occurred in that part of west-central<br />
Saskatchewan that is downwind of the rapidlyexpanding<br />
oil sand industry (as illustrated in Figure 37).<br />
Regional critical load exceedances ranged from<br />
54.5 to 909 eq/ha/yr, with the largest (positive) values<br />
occurring close to base metal smelters in Manitoba<br />
or downwind of the oil sands operations in western<br />
Alberta (Figure 38). The exceedances were almost<br />
entirely due to sulphate deposition. Nitrogen inputs<br />
to the lakes, while signifi cant, were virtually entirely<br />
6<br />
Canada-United.States. 1983. Memorandum of intent on transboundary air pollution. <strong>Report</strong> of the Impact Assessment Working Group I,<br />
Section 3-Aquatic Effects. 259 p.<br />
7<br />
Jeffries, DS, Semkin, RG, Gibson, JJ, Wong, I. <strong>2010</strong>. Recently surveyed lakes in northern Manitoba and Saskatchewan, Canada:<br />
characteristics and critical loads of acidity. J Limnol 69(Suppl. 1):45-55.<br />
66