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FINAL REPORT - International Joint Commission

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Performance Indicators<br />

As noted earlier, the Environmental Technical Work Group initially established over 400 performance<br />

indicators for assessing impacts of levels and flows. It quickly became apparent that 400 performance<br />

indicators were far too many for the Study Board to make sense of. Through an extensive process that<br />

involved using the IERM to evaluate the response of all 400 performance indicators to alternative<br />

plan/supply scenarios, a subset of 32 key performance indicators was identified on the basis of the<br />

following criteria:<br />

ANNEX 2<br />

• Significance – the performance indicators must show some key importance to the ecosystem<br />

and region;<br />

• Certainty – there must be confidence in the performance indicators’ results;<br />

• Sensitivity – the performance indicators must be significantly affected by the changes in levels and<br />

flows generated by the alternative regulation plans and/or supply scenarios being tested.<br />

Performance indicators were also grouped based on similar responses to water levels and flows. In other<br />

words, each key indicator may represent a number of other indicators that behave similarly. The 32 key<br />

performance indicators selected for primary use in comparing and evaluating alternative regulation plans<br />

are presented in tables A-1 and A-2. It was these 32 key performance indicators that were used by the<br />

Study Board in the plan evaluation process. Descriptions of each of the key performance indicators,<br />

including comments on certainty, sensitivity and significance, are included in the Integrated Environmental<br />

Response Model documentation (Limno-Tech, 2005).<br />

Even with this reduction in performance indicators, the Study Board still needed some way of comparing<br />

the different performance indicator metrics (e.g., area of wetland vs. productivity, vs. reproduction indices).<br />

It was important to adopt an approach that could be used to effectively compare the responses of many<br />

indicators to alternative regulation plans. A performance indicator “ratio” approach was developed<br />

collaboratively by Limno-Tech Inc. and the Environmental Technical Work Group to provide a means for<br />

rapidly evaluating plan responses. The response ratios are defined in such a way that it is easy to establish<br />

which plan is “better” in terms of each indicator by comparing the ratio with 1.00, where 1.00 is the<br />

environmental response under the baseline plan 1958-DD, anything greater than 1.00 represents an<br />

improvement, and anything below 1.00 a deterioration relative to 1958-DD. For example, a score of<br />

1.44 would indicate that a performance indicator performed 44% better under the evaluated plan than<br />

under 1958-DD. The Study Board stipulated that all plans were to be measured against Plan 1958-DD as<br />

the baseline plan, but the Environmental Technical Work Group also used the Pre-project Plan in its<br />

comparisons to serve as the natural reference condition.<br />

Options for Managing Lake Ontario and St. Lawrence River Water Levels and Flows<br />

21

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