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Two types <strong>of</strong> <strong>decision</strong> (i.e., for <strong>planning</strong> <strong>and</strong> operation) are shown in the left column. These generally<br />

conform <strong>to</strong>: a) the strategic assessment <strong>and</strong> project preparation <strong>and</strong> b) the project implementation <strong>and</strong><br />

project operation phases <strong>of</strong> the project cycle (IHA 2009a), respectively. Table 4.1 provides an overview <strong>of</strong> the<br />

<strong>decision</strong> making processes <strong>to</strong> which DSSs can contribute at the different stages <strong>of</strong> the <strong>decision</strong> making cycle.<br />

Table 4.1 Examples <strong>of</strong> processes <strong>to</strong> which DSSs can contribute at different stages <strong>of</strong> the <strong>decision</strong> making cycle.<br />

Planning DSSs Operational DSSs<br />

Strategic assessment Project preparation Project<br />

implementation<br />

Project operation<br />

• Water <strong>and</strong><br />

energy needs<br />

assessment<br />

• Basin master<br />

plan<br />

• Strategic<br />

environmental<br />

assessment<br />

• Life cycle<br />

analyses <strong>of</strong><br />

different options<br />

22<br />

• Comprehensive<br />

options assessment<br />

• Environmental<br />

<strong>and</strong> health impact<br />

assessment<br />

• Social impact<br />

assessment<br />

• Economic/financial<br />

viability assessment<br />

• Dam design<br />

<strong>and</strong> plans for<br />

operation<br />

• Development <strong>of</strong><br />

environmental,<br />

health <strong>and</strong> social<br />

management<br />

plans<br />

• Dam operating rules<br />

<strong>and</strong> pro<strong>to</strong>cols<br />

• Implementation<br />

<strong>of</strong> environmental,<br />

health <strong>and</strong> social<br />

management plans<br />

The framework conceptualizes the <strong>decision</strong> making process stepping through four major sets <strong>of</strong> activities:<br />

technical, stakeholder, political <strong>and</strong> management (second column on left). None <strong>of</strong> these four sets <strong>of</strong><br />

activities is exclusive <strong>to</strong> the particular group which is used <strong>to</strong> designate it, but each is seen as the dominant<br />

“ac<strong>to</strong>r” at that particular stage in the project cycle. At each stage, the <strong>decision</strong> makers <strong>and</strong> their information<br />

requirements vary. For example, <strong>decision</strong>s about whether or not a <strong>dam</strong> should be built usually reside with<br />

politicians whilst <strong>decision</strong>s on day-<strong>to</strong>-day operation (requiring very different information) will be made by<br />

the <strong>dam</strong> opera<strong>to</strong>r.<br />

4.3 Planning<br />

The <strong>decision</strong> making process is initiated by a needs assessment. In relation <strong>to</strong> <strong>dam</strong>s this relates primarily<br />

<strong>to</strong> likely future dem<strong>and</strong>s for water <strong>and</strong>/or energy services across a range <strong>of</strong> stakeholders. Following a needs<br />

assessment a range <strong>of</strong> options should be considered for fulfilling the dem<strong>and</strong>s. An options assessment<br />

comprises the collation <strong>and</strong> evaluation <strong>of</strong> all possible alternatives <strong>to</strong> meet the defined needs. In assessing<br />

options it is important that not only future dem<strong>and</strong>s but also the wider development objectives <strong>of</strong> a country<br />

or region are taken in<strong>to</strong> account. Consequently, options assessments must also include assessment <strong>of</strong> the<br />

likely wider socioeconomic <strong>and</strong> environmental impacts, as well as issues <strong>of</strong> equity, poverty alleviation, etc.<br />

In many instances, evaluation <strong>of</strong> options for the management <strong>of</strong> water resources will be best performed<br />

at the river basin level (e.g., through the development <strong>of</strong> a basin master plan). This should seek <strong>to</strong> balance<br />

competing uses <strong>of</strong> finite water resources <strong>and</strong> seek cross-linkages between different dem<strong>and</strong>s. Ideally, a range<br />

<strong>of</strong> stakeholders (including representatives <strong>of</strong> basin communities) should contribute <strong>to</strong> the development<br />

<strong>of</strong> basin master plans. In Africa, where many basins cross international borders, water resource option<br />

assessments should take in<strong>to</strong> account the needs <strong>of</strong> all riparian countries. For <strong>dam</strong>s, whether or not they are<br />

located in transboundary basins, options assessments will <strong>of</strong>ten result in multifunctional projects that should<br />

be more sustainable. Ideally, the options assessment should lead <strong>to</strong> the identification <strong>of</strong> a list <strong>of</strong> prioritized

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