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Research Papers

Economic and environmental tradeoffs from alternative water allocation policies in the South Saskatchewan River Basin

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Pages 409-420 | Received 02 Jul 2014, Accepted 06 Jul 2014, Published online: 23 Oct 2014

Figures & data

Figure 1. Map of irrigation districts within the South Saskatchewan River Basin.

Figure 1. Map of irrigation districts within the South Saskatchewan River Basin.

Figure 2. The South Saskatchewan River Basin (SSRB) in Aquarius. The SSRB is represented in Aquarius as a network of approximately 70 demand and supply nodes. This figure provides a snapshot of how the network is modeled in the SSRB with diversion points and return flows along the reach. ID: irrigation district; IFN: instream flow needs; WCO: water conservation objective.

Figure 2. The South Saskatchewan River Basin (SSRB) in Aquarius. The SSRB is represented in Aquarius as a network of approximately 70 demand and supply nodes. This figure provides a snapshot of how the network is modeled in the SSRB with diversion points and return flows along the reach. ID: irrigation district; IFN: instream flow needs; WCO: water conservation objective.

Table 1. The Aquarius model was calibrated to the 2001 drought to understand the vulnerability of the South Saskatchewan River Basin (SSRB). Natural flows are shown as a percentage of long-term average per sub-basin.

Table 2. Comparison of economic efficiency of the initial allocation rules. Economic benefits improve under a share rule, but the system only achieves 56% of potential economic value.

Table 3. Diversion and consumption by use (Mm3). This illustrates how water is allocated between municipal and irrigation licensees under each of the four scenarios. The first column under each sub-basin shows the amount of water diverted (div.), while the second column shows the amount of water consumed (con.).

Table 4. Monthly marginal values for selected uses by scenario (CAD$2013). By showing the marginal values of different uses at the solution, it is found that municipal uses have a higher marginal value than agricultural uses. This Alberta phenomenon is consistent with water trades in the US where water is typically transferred from agricultural to municipal uses (Brown Citation2006).

Table 5. Violation of instream flow needs (IFN) and water conservation objective (WCO) constraints per allocation scenario.

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