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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

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