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MEASURING WATER USE IN A GREEN ECONOMY - UNEP

MEASURING WATER USE IN A GREEN ECONOMY - UNEP

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Measuring water use in a green economy<br />

The following subsections provide details on<br />

these methodologies.<br />

4.1 Water registers<br />

In most parts of the world, the development<br />

of water availability and access registers is in<br />

its infancy. The same is true of systems that<br />

enable the efficient management of allocations<br />

during times of scarcity.<br />

Rather than developing registers and systems<br />

in isolation from more general wateraccounting<br />

arrangements, it is possible to<br />

develop them so that they become the primary<br />

source of information about how, where and<br />

when water may be and is used.<br />

It is then possible to construct registers and<br />

systems that can be used to help introduce<br />

water charging systems and develop<br />

arrangements that allow the transfer of<br />

entitlements and allocations from one user<br />

to another. For these systems to work well,<br />

however, there is a need for institutional rigour<br />

and administrative arrangements that ensure<br />

compliance with allocation arrangements.<br />

In fully allocated systems, it is critical that<br />

whenever one person is allowed to take more<br />

water, parallel arrangements are put in place to<br />

ensure that someone else takes less.<br />

Systems built in this manner typically begin by<br />

partitioning a water resource into a number<br />

of ‘pools’ of differing allocation priorities.<br />

Entitlements to access water allocated to<br />

each pool are then distributed among users<br />

or user groups. As the volume of water within<br />

these pools is likely to change from season to<br />

season, each entitlement is defined as a share<br />

of any water allocated to the pool. Sustainable<br />

diversion limits are set for each pool in a<br />

manner that ensures that enough water is<br />

set aside for conveyance, maintaining the<br />

environment and meeting other needs.<br />

4.1.1 Pools<br />

The approach to defining each watermanagement<br />

‘pool’ requires careful<br />

consideration. For a surface water system, the<br />

approach typically involves:<br />

• a pool of sufficient size to maintain enough<br />

base flows to convey water to the end of the<br />

system (Poff et al., 2010). This base flow<br />

provides benefits to all entitlement holders<br />

and also for non-consumptive uses like<br />

recreation and transport;<br />

• one or more consumptive pools. In some<br />

situations, it is appropriate to establish<br />

pools of varying reliability, for example,<br />

to give a city a much more reliable water<br />

supply than a dairy farmer;<br />

• when entitlement systems are put in<br />

place, it is normally necessary to define<br />

and manage flood waters and flood risks<br />

outside the entitlement system;<br />

• when a shared system is used to define<br />

entitlements and the degree of compliance<br />

with entitlements is high, it is possible to<br />

use market arrangements to encourage<br />

each group of users to manage risks<br />

associated with climate change. However,<br />

an appropriate governance mechanism<br />

may be necessary to correct socially<br />

iniquitous effects of the market.<br />

Intense stakeholder dialogue and riskmanagement<br />

arrangements are necessary<br />

to ensure that all water users and relevant<br />

stakeholders understand the complexity of the<br />

hydrological system, including how rivers and<br />

aquifers interact with each other or how adverse<br />

climate change, or alterations of policy, are likely<br />

to affect the value of their access entitlement<br />

and allocations of water. System-wide planning<br />

arrangements are needed to specify how water<br />

is allocated to the environment and all other<br />

users, and to each pool.<br />

Good data is needed to prioritise water uses<br />

efficiently and equitably: the Murray Darling<br />

Basin in Australia provides one of several<br />

examples (See Box 4.1).<br />

47

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