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MEASURING WATER USE IN A GREEN ECONOMY - UNEP

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3 Data and information<br />

sources<br />

The core elements of any methodology<br />

and information system needed to quantify<br />

how water flows through the hydrological<br />

system, ecosystems, and the economy are<br />

the water inventory and temporal and spatial<br />

assessment of the stocks and flows in and<br />

through the different compartments. The data<br />

flows and methodologies needed to tackle the<br />

challenges of sustainable water management<br />

need to be temporally and spatially specific<br />

and need to address both the environmental<br />

impacts and the socio-economic dimension<br />

of water efficiency. It is also vital that the<br />

sources of data and information become<br />

well-established, along with the governance<br />

structures that use them. Given the complexity<br />

of management of freshwater today, the focus<br />

of this report remains for the most part on<br />

water resources on land. There are, however,<br />

certain considerations to be made with respect<br />

to some coastal and transitional ecosystems,<br />

e.g. coconut groves and mangroves, which rely<br />

on seawater to provide ecosystem services on<br />

land. Where these occur, they are included in<br />

the quantitative methods described below.<br />

3.1 Elements of the water<br />

balance<br />

All methodologies that quantify relevant<br />

aspects of the hydrological and economic<br />

water cycle rely on sound basic data. Water<br />

balances (also known as inventories or<br />

registers) represent the fundamental approach<br />

to accounting for the flow of water into and out<br />

of a system. But to provide a robust basis for<br />

analysis and decision-making, such accounts<br />

must meet certain criteria.<br />

When considering resource efficiency and<br />

sustainable use, a hydrological balance must<br />

include fluxes (flows available for immediate<br />

use) and stocks (resource from past inputs) but<br />

not future inputs. Future resources must not be<br />

treated as currently exploitable. That means,<br />

for example, that the time span for allocations<br />

has to be chosen carefully. Availability and<br />

accessibility shall be evaluated on a monthly<br />

basis, depending on the specific climatic<br />

variability in the eco-regions and catchments.<br />

A seasonality signal may be stronger and<br />

therefore can be used instead. Classical water<br />

balances, which calculate an overall balance<br />

over one year or over national territories larger<br />

than natural hydrological units, may ignore<br />

this point and should therefore be used with<br />

caution.<br />

The key components of the hydrological balance<br />

have been specified since the second half of<br />

the 20th century: evaporation, precipitation,<br />

soil water, transfers to groundwater and<br />

rivers, storage in lakes, aquifers and ice<br />

caps. In classical balances, the volume in a<br />

certain compartment is presented without<br />

reference to its residence time, which can vary<br />

significantly between different compartments.<br />

For example, the global average residence<br />

time in oceans (standing stock 1 370 million<br />

km 3 ) is approximately 2 600 years, whereas in<br />

rivers (standing stock 0.0012 million km 3 ) the<br />

average residence time is 12 days. The main<br />

elements of the water balance are shown in<br />

34

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