Surface water diversions
Water can be diverted from surface water resources in a number of ways including:
- major diversions by water supply companies for distributed
supply systems to urban, rural, commercial or industrial users
- private diversions directly from a stream or waterbody by
individual users, either for direct use or to fill a storage for later use
- on-stream or catchment storages that capture runoff or impede
the flow in a stream or prevent water from reaching the stream or waterbody
further downstream in a catchment.
AWR 2005 defines diversions and extractions differently to water use. Water
use is the end use or application of the water supplied, in terms of how it
is used by the end user (e.g. water used for horticulture or industrial use).
This is different to diversions and extractions, which define the water that
is delivered, either through a reticulated system (supplied by an authority
or company), or extracted by the landholder (through a groundwater bore or
from pumping from an adjacent stream). The Australian Bureau of Statistics
is compiling a comprehensive report on water use in Australia at a national,
state and territory perspective and at a more detailed level for selected
water management areas.
The availability of data on the level of surface water diversions varies greatly
across Australia and tends to be best in regulated catchments with major water
supply infrastructure, or in regions where requirements exist for water supply
utilities and bulk suppliers to report diversion figures to state, territory
or Australian government authorities. Conversely, the availability of data
on surface water diversions in unregulated catchments is poor and, where available,
is usually a rough estimate that is based on licence volumes or areas. Only
a small proportion of surface water diversions are metered across the country,
but metering programmes are currently being planned and implemented in most
states and territories (where surface water diversions are significant).
The accompanying map shows the data provided on surface water diversions across
Australia . Data are available for most of Australia , apart from approximately
half of Queensland and New South Wales . There are no surface water diversion
data for most of the unregulated surface water management areas in New South
Wales , even though the surface water diversion in these areas is expected
to be significant. Non-consumptive diversions (e.g. hydro-electricity) have
not been included in the Tasmanian surface water diversion figures. In addition,
in many parts of Australia (e.g. most of Western Australia, South Australia
and the Northern Territory), the surface water diversions are minimal and hence
the values shown in the accompanying map are estimates that are based on jurisdiction-supplied
information for the purpose of creating a complete picture across Australia based on the data provided for the Level 1 Assessment by the states and territories.
Refer also to the tables below.
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Surface water diversions July 2004 - June 2005 |
Download high resolution Map:
Surface water diversions July 2004 - June 2005 (1.6 Meg )
(this document requires the use of Adobe Acrobat
Reader )
Interactive Maps:
Click on the links below to create and customise your own versions of the maps (e.g.
add or remove layers) using the Map Maker tool on the Australian Natural Resource
Atlas website:
Number of surface water management areas where surface
water diversions are determined from metered data
|
|
|
ACT |
NSW |
NT |
QLD |
SA |
TAS |
VIC |
WA |
National |
|
1 |
12 |
38 |
19 |
65 |
46 |
28 |
36 |
245 |
|
0 |
0 |
15 |
0 |
0 |
46 |
0 |
24 |
85 |
|
0 |
0 |
0 |
0 |
0 |
0 |
6 |
0 |
6 |
|
0 |
0 |
1 |
0 |
0 |
0 |
5 |
0 |
6 |
|
0 |
0 |
0 |
0 |
0 |
0 |
7 |
0 |
7 |
|
0 |
0 |
0 |
0 |
0 |
0 |
3 |
0 |
3 |
|
1 |
12 |
1 |
0 |
1 |
0 |
7 |
0 |
22 |
|
0 |
0 |
21 |
19 |
64 |
0 |
0 |
12 |
116 |
Method
used for determining surface water diversion for 200405 ( if NOT 100 percent
metered)
|
|
|
ACT |
NSW |
NT |
QLD |
SA |
TAS |
VIC |
WA |
National |
|
0 |
10 |
0 |
0 |
2 |
0 |
29 |
20 |
61 |
|
0 |
2 |
10 |
0 |
3 |
43 |
29 |
20 |
107 |
|
0 |
0 |
0 |
0 |
0 |
3 |
0 |
0 |
3 |
|
0 |
0 |
0 |
0 |
0 |
0 |
29 |
0 |
29 |
|
0 |
2 |
23 |
0 |
1 |
3 |
29 |
14 |
72 |
Note: the sum of the methods used may be more than the number of surface water
management areas that are not metered, because more than one calculation method
was used for individual surface water management areas in some cases.
All of the surface water diversion data provided for Queensland surface water
management areas are reported from metered data, but not all diversions are
currently metered. As a result, the figures provided for Queensland do not
include all diverters. Water meter data is not yet available for any of Tasmania
's surface water management areas. The diversion figures for most (43 of 48)
of surface water management areas in Tasmania were estimated from licence volumes
and for the remaining five surface water management areas of the state, the
surface water diversions were estimated from power usage for pumps.
In Victoria , about a third of surface water management areas determined their
surface water diversions by using metered data; the rest of the surface water
management areas had a small proportion of metered data available. The impact
from catchment farm dams (minor catchment storages) was estimated based on
the outcomes of the Sustainable Diversion Limit Project, which estimated the
volume of all catchment farm dams across Victoria (thereby enabling an estimate
of use from farm dams based on a proportion of licence volume). Models to estimate
surface water diversions were also used in some surface water management areas
in Victoria .
There is currently no metering of surface water diversions in Western Australia
, and the methods used to estimate surface water diversion included using estimated
unlicensed diversion and, in some cases unused licence allocation.
While a large proportion of surface water diversions (in number terms) are
not metered across Australia , most of the major (by volume) diversions are
metered. In New South Wales, for example, the regulated systems are well metered
and they represent the majority of water diversions by volume, whereas the
unregulated systems are not well metered and can have many users (spread out
over large geographical areas), but they are only a small proportion of the
total diversions.
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