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ASIAN PACIFIC FRIEND |
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Map of the River

AUSLIG, Australia’s National Mapping Agency
Table of Basic Data
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Name: Burdekin River |
Serial No: Australia - 1 |
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Location: North Queensland, Australia |
E144° 0' - 149° 0' |
S18° 0'- 25° 0' |
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Area: 130 000km2 |
Length of the main stream: 732km |
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Origin: Seaview (745m), Gorge Ranges (926m) |
Highest Pt: Commissioners Cap, Great Dividing Range (1028m) |
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Outlet: Coral Sea, South Pacific Ocean |
Lowest Pt: River mouth at sea level (0m) |
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Main Base Rocks: Pre-Cambrian to Cainozoic; Mudstone, Granite, Alluvium, Gravels and Conglomerate, Limestone, Sandstone, Siltstone. |
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Main tributaries: Clarke River (6760km2), Star River (1990km2) Basalt River (2900km2), Suttor River (73 700km2), Belyando River (tributary of the Suttor River) 35 720km2), Bowen-Broken River (9530km2), Bogie River (2250km2) |
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Main reservoirs: Burdekin Falls Dam (1860 x106m3, 1987), Eungella Dam, (131x106m3, 1969) |
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Mean annual precipitation: 670mm |
Mean annual runoff: 322m3/s (at Clare, 1951-1992) |
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Population: 23 400 (1991),(Main towns only) |
Main towns: Charters Towers, Ayr, Home Hill, Collinsville |
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Land Use: Grazing (beef) 95%, Agriculture (sugar cane, maize, vegetables) 4%,. Mining (coal, gold), 1% (1991) |
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1.1 General Description
The Burdekin River is located in the drier part of the tropics on Queensland's east coast. Diverse landscapes are represented in this catchment (basin). There is a high variability of rainfall within any one year, and from year to year. The average annual precipitation for the catchment is 670mm. The catchment is 130 000km2 in area and approximately 732km long. The Burdekin River has its source in the Seaview and Gorge Ranges and flows 550km south-east to a latitude of approximately S20° 40'. The river then changes direction to flow a further 150km in a northerly direction then turns almost due east before discharging into the Pacific Ocean at Ayr. The coastal plains are narrow and discontinuous, but widen toward the lower reaches. The maximum width of the coastal region is 56km and lies within the delta plain - an area that is prone to widespread flooding.
Beef cattle is the most widespread form of grazing and is a major industry in the upper Burdekin region with much of the available land used for this purpose. Irrigated crop production in this region is generally restricted to small scale operations for the purpose of providing feed for cattle. Mining of gold and coal continues to have a major influence in the region's economy. Agricultural development in the delta is predominantly sugarcane.
The Burdekin River has one of the most diverse fish populations of all Queensland rivers. Protection of the fish and invertebrate fauna relies on the maintenance of the various ecosystems along the river. The Queensland Government has recognised that future weir development in the Burdekin River should include consideration of fish populations from an ecological viewpoint and as a recreational resource.
The Burdekin Falls Dam, completed in 1987, has a storage capacity of 1860 x 106 m3. The Dam forms Lake Dalrymple, covering an area of 22 400 hectares and ponds water for 50 kilometres up the Burdekin River.
2. Geographical Information
2.1 Land Use Map

AUSLIG, Australia’s National Mapping Agency
2.2 Characteristics of the River and the Main Tributaries
|
No |
Name of river |
Length [km] Catchment Area [km2] |
Highest Peak [m] Lowest Point [m] |
Cities population [1991] |
Land use [%] |
|
1 |
Burdekin River (Main River) |
732 130 000 |
Commissioners Cap (1028) Sea level (0) |
Ayr (8637) Home Hill (3197) Charters Towers (9016) |
G(95%), A(4%) U&M(1%) |
|
2 |
Clarke River (Tributary) |
190 6470 |
1012 400 |
G(100%) |
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|
3 |
Star River (Tributary) |
81 2010 |
Paluma Range (1030) 365 |
G(100%) |
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|
4 |
Basalt River (Tributary) |
160 2900 |
857 300 |
G(100%) |
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5 |
Suttor River (Tributary) |
337 73 303 |
Denham Range (590) 150 |
G(100%) |
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6 |
Belyando River (Tributary of the Suttor R) |
393 35 720 |
Drummond Range (680) 200 |
G(100%) |
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|
7 |
Bowen-Broken River (Tributary) |
208 9530 |
Clarke Range (950) 50 |
Collinsville (2552) |
G(90%), M(10%) |
|
8 |
Bogie River (Tributary) |
130 2250 |
720 45 |
G(100%) |
A: Agriculture (sugar cane), F: Forest, G: Grazing (cattle), M: Mining, U: Urban.
2.3 Longitudinal Profiles

3. Climatological Information
3.1 Annual Isohyetal Map and Observation Stations

Based on the data of Department of Primary Industries, Water Resources, Queensland Isohyetal map was made by interpolating 42 long term stations in the catchment between 1920-1969 taking into account topography and synoptic variations.
3.2 List of Meteorological Observation Stations
The table of meteorological stations below is a selection of the main stations in the catchment.
|
No. |
Station |
Elevation [m] |
Location |
Observation period |
Mean annual precipitation [mm] |
Estimated Mean annual evaporation [mm] |
Observation items 1) |
||||
|
030040 |
Pentland |
403 |
S20° 31' E145° 24' |
1885-1993 |
673 |
2210 |
P |
||||
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030052 |
Wando Vale |
560 |
S19° 40' E144° 53' |
1890-1993 |
675 |
2200 |
P |
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030082 |
Gregory Springs |
732 |
S19° 43' E144° 23' |
1927-1993 |
735 |
2300 |
P(TSP) |
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030083 |
Toomba |
380 |
S19° 58' E145° 35' |
1960-1993 |
620 |
2110 |
P |
||||
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030137 |
Hillgrove |
300 |
S19° 38' E145° 47' |
1899-1993 |
544 |
2100 |
P |
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032040 |
Townsville |
4 |
S19° 15' E146° 46' |
1940-1993 |
1137 |
2395 |
T, P, E, SR, DS |
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032063 |
Blue Range |
348 |
S19° 10' E145° 25' |
1953-1993 |
681 |
2050 |
P(TSP) |
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032064 |
Paluma |
892 |
S19° 00' E146° 12' |
1969-1993 |
2618 |
2000 |
P(TSP) |
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|
032122 |
Greenvale |
427 |
S18° 59' E145° 07' |
1890-1993 |
643 |
2150 |
P |
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|
033001 |
Ayr |
11 |
S19° 34' E14° 24' |
1886-1993 |
1083 |
2071 |
T, P, E, DS |
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033013 |
Collinsville |
187 |
S20° 30' E147° 13' |
1939-1993 |
726 |
1931 |
T,P(TSP),E |
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033032 |
Home Hill |
20 |
S19° 40' E147° 25' |
1924-1993 |
952 |
2130 |
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033051 |
Mingela |
289 |
S19° 53' E146° 38' |
1899-1993 |
655 |
2050 |
P |
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033062 |
Ravenswood |
249 |
S20° 06' E146° 53' |
1871-1993 |
683 |
2000 |
P |
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033090 |
Millaroo |
45 |
S20° 03' E147° 16' |
1965-1985 1991-1993 |
841 |
1841 |
T, P, E, DS |
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033122 |
Clare |
26 |
S19° 47' E147° 13' |
1895-1993 |
833 |
2100 |
P |
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033139 |
Paynes Lagoon |
305 |
S19° 28' E146° 07' |
1969-1993 |
593 |
2100 |
P |
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033205 |
Dalbeg |
60 |
S20° 16' E147° 18' |
1954-1993 |
764 |
1980 |
P |
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033227 |
Havilah |
140 |
S20° 48' E147° 50' |
1935-1993 |
637 |
1980 |
P |
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034000 |
Balfes Creek |
327 |
S20° 13' E145° 55' |
1889-1993 |
630 |
2120 |
P |
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034002 |
Charters Towers |
310 |
S20° 05' E146° 16' |
1882-1992 |
660 |
2035 |
T, P, E |
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034006 |
Mt Coolon |
240 |
S21° 23' E147° 20' |
1925-1993 |
580 |
2000 |
P |
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034007 |
Mt McConnell |
457 |
S20° 48' E146° 59' |
1899-1993 |
647 |
2050 |
P |
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034017 |
Broadleigh Downs |
244 |
S20° 55' E146° 11' |
1962-1993 |
614 |
2150 |
P |
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034020 |
Wollombi |
274 |
S21° 21' E147° 50' |
1965-1993 |
516 |
2000 |
P |
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034022 |
Mt Douglas |
170 |
S21° 31' E146° 53' |
1912-1993 |
603 |
2140 |
P |
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034049 |
Doongara |
300 |
S20° 34' E146° 29' |
1968-1993 |
652 |
2120 |
P |
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034085 |
Sellheim |
240 |
S20° 01' E146° 25' |
1897-1993 |
613 |
2050 |
P |
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034087 |
Scartwater |
190 |
S21° 06' E146° 53' |
1949-1993 |
609 |
2100 |
P |
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035000 |
Alpha |
350 |
S23° 39' E146° 38' |
1886-1993 |
564 |
2350 |
P(TSP) |
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035094 |
Carrols Creek |
305 |
S22° 30' E147° 31' |
1962-1993 |
584 |
2170 |
P |
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|
035275 |
Islay Plains |
300 |
S23° 13' E146° 53' |
1988-1993 |
596 |
2310 |
P |
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|
036010 |
Bulliwallah |
305 |
S21° 57' E146° 38' |
1912-1993 |
601 |
2200 |
P |
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036050 |
Ulcanbah |
270 |
S22° 02' E145° 59' |
1887-1993 |
559 |
2320 |
P |
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036055 |
Dunrobin |
340 |
S22° 41' E146° 09' |
1972-1993 |
511 |
2360 |
P |
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036071 |
Moray Downs |
210 |
S21° 37' E146° 38' |
1914-1993 |
563 |
2230 |
P |
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036083 |
Albro |
255 |
S22° 42' E146° 34' |
1970-1993 |
573 |
2300 |
P |
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036089 |
Bygana |
270 |
S22° 12' E146° 33' |
1946-1993 |
581 |
2290 |
P |
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|
036159 |
Beresford |
280 |
S22° 30' E146° 56' |
1987-1993 |
471 |
2260 |
P |
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|
036160 |
Frankfield |
240 |
S22° 16' E147° 06' |
1987-1993 |
541 |
2200 |
P |
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All rainfall stations shown are operated by the Australian Bureau of Meteorology.
1) T: Temperature P: Precipitation TB
= tipping bucket with digital data logger
TSP = tilting syphon pluviograph with
recording chart E: Evaporation
SR: Solar radiation DS: Duration
of sunshine
3.3 Monthly Climate Data
The tables below show climatic data for selected stations in and adjacent to the Burdekin catchment.
The Townsville station is just outside the catchment but is included because of the full range of data recorded.
Station: Townsville (Station 032040)
|
Observation parameter |
Jan
|
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
Annual |
Period for the mean |
|
Temperature [° C] |
27.6 |
27.1 |
26.6 |
25.0 |
22.4 |
19.9 |
19.2 |
20.4 |
22.3 |
25.0 |
26.8 |
27.7 |
24.2 |
1941-93 |
|
Precipitation [mm] |
274 |
291 |
205 |
66 |
37 |
22 |
15 |
12 |
11 |
23 |
54 |
127 |
1137 |
1940-93 |
|
Evaporation [mm] |
257 |
226 |
217 |
202 |
174 |
158 |
164 |
195 |
248 |
282 |
291 |
285 |
2700 |
1970-73 |
|
Solar radiation [MJ/m2/day] |
21.4 |
20.0 |
20.0 |
17.2 |
15.2 |
14.7 |
15.8 |
18.2 |
22.0 |
24.3 |
24.6 |
23.4 |
19.7 |
1971-91 |
|
Duration of sunshine [hrs] |
242 |
223 |
229 |
239 |
226 |
245 |
260 |
282 |
295 |
304 |
291 |
276 |
3112 |
1958-93 |
Station: Ayr (Station 033001)
|
Observation parameter |
Jan
|
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
Annual |
Period for the mean |
|
Temperature [° C] |
27.4 |
27.0 |
26.0 |
24.2 |
21.9 |
20.4 |
18.2 |
19.4 |
21.4 |
23.7 |
25.8 |
26.9 |
23.6 |
1952-93 |
|
Precipitation [mm] |
264 |
262 |
186 |
63 |
38 |
32 |
19 |
15 |
21 |
23 |
44 |
116 |
1083 |
1886-1993 |
|
Evaporation [mm] |
205 |
192 |
177 |
155 |
130 |
118 |
124 |
146 |
167 |
211 |
223 |
223 |
2071 |
1970-93 |
|
Duration of sunshine [hrs] |
248 |
220 |
220 |
226 |
223 |
236 |
248 |
267 |
279 |
291 |
273 |
264 |
2995 |
1965-93 |
Station: Collinsville (Station 033013)
|
Observation parameter |
Jan
|
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
Annual |
Period for the mean |
|
|
Temperature [° C] |
27.3 |
27.1 |
25.8 |
23.4 |
20.4 |
17.5 |
16.7 |
18.6 |
21.4 |
24.5 |
26.7 |
27.3 |
23.1 |
1956-81 1991-93 |
|
|
Precipitation [mm] |
136 |
155 |
107 |
46 |
37 |
27 |
22 |
14 |
11 |
21 |
53 |
97 |
726 |
1939-93 |
|
|
Evaporation [mm] |
189 |
180 |
167 |
146 |
112 |
90 |
102 |
133 |
167 |
205 |
223 |
217 |
1931 |
1972-93 |
|
Station: Millaroo (Station 033090)
|
Observation parameter |
Jan
|
Feb |
Mar |
Apr |
May |
Jun |
July |
Aug |
Sep |
Oct |
Nov |
Dec |
Annual |
Period for the mean |
|
Temperature [° C] |
28.1 |
27.4 |
26.4 |
24.2 |
21.4 |
18.3 |
17.7 |
19.5 |
21.7 |
24.2 |
26.8 |
27.5 |
23.6 |
1965-85 1991-93 |
|
Precipitation [mm] |
191 |
165 |
127 |
49 |
47 |
20 |
16 |
10 |
9 |
25 |
57 |
125 |
841 |
1953-93 |
|
Evaporation [mm] |
180 |
161 |
152 |
130 |
109 |
96 |
105 |
130 |
158 |
195 |
214 |
211 |
1841 |
1970-85 1991-93 |
|
Duration of sunshine [hrs] |
233 |
217 |
214 |
229 |
229 |
245 |
254 |
267 |
282 |
295 |
291 |
254 |
3010 |
1965-85 1991-93 |
Station: Charters Towers (Station 034002)
|
Observation parameter |
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
Annual |
Period for the mean |
|
Temperature [° C] |
28.0 |
27.4 |
26.1 |
24.0 |
21.1 |
18.4 |
17.8 |
20.0 |
22.1 |
25.1 |
27.2 |
28.0 |
23.8 |
1907-92 |
|
Precipitation [mm] |
137 |
130 |
104 |
43 |
24 |
27 |
17 |
13 |
15 |
22 |
41 |
87 |
660 |
1882-1992 |
|
Evaporation [mm] |
210 |
170 |
175 |
150 |
130 |
105 |
115 |
140 |
170 |
210 |
230 |
230 |
2035 |
1970-92 |
Evaporation pan used: - US Class A (48 inch dia)
3.4 Long-term variation of Monthly Precipitation Series
Graphs of two long term precipitation series are shown below:
a) Alpha (Station 035000)

b) Charters Towers (Station 034002)

4. Hydrological Information
4.1 Map of Streamflow Observation Stations
(Map is missing)
4.2 List of Hydrological Observation Stations
The table of hydrological stations below is a selection of the main stations in the catchment.
|
No. |
Station |
Location |
Elevation [m] |
Catchment area (A) [km2] |
Observation period |
Observation items 1) |
|
120001 |
Burdekin River at Home Hill |
S19° 40' E147° 21' |
3 |
130 000 |
1922-1956 |
H2, Q |
|
120002 |
Burdekin River at Sellheim |
S20° 00' E146° 26' |
215 |
36 400 |
1947-1968 1968-1994 |
H2, Q H1, Q |
|
120004 |
Burdekin River at Falls (D/S) |
S20° 39' E147° 09' |
120 |
114 220 |
1948-1967 1967-1985 |
H2, Q H1, Q |
|
120006 |
Burdekin River at Clare |
S19° 46' 147° 15' |
9 |
129 500 |
1950-1975 1975-1994 |
H2, Q H1, Q |
|
120008 |
Burdekin River at Dalbeg |
S20° 19' E147° 18' |
34 |
126 000 |
1954-1975 1975-1994 |
H2, Q H1, Q |
|
120010 |
Burdekin River at 64.4km |
S19° 58' E147° 15' |
19 |
129 000 |
1959-1986 |
H1, Q |
|
120015 |
Burdekin River at Hydro Site |
S20° 38' E147° 10' |
79 |
114 000 |
1977-1994 |
H1, Q |
|
120101 |
Burdekin River at Charters Towers |
S19° 58' E146° 18' |
227 |
35 000 |
1915-1952 |
H2, Q |
|
120105 |
Clarke River at Telegraph Station |
S19° 13' E145° 26' |
344 |
6720 |
1949-1975 |
H2, Q |
|
120107 |
Burdekin River at Blue Range |
S19° 10' E145° 25' |
348 |
10 500 |
1952-1982 1982-1989 |
H2, Q H1, Q |
|
120110 |
Burdekin River at Mount Fullstop |
S19° 12' E145° 30' |
336 |
17 420 |
1965-1990 |
H1, Q |
|
120111 |
Burdekin River at Lucky Downs |
S18° 53' E144° 58' |
11 |
6130 |
1967-1988 |
H1, Q |
|
120112 |
Star River at Laroona |
S19° 23' E146° 03' |
295 |
1205 |
1967-1989 |
H1, Q |
|
120121 |
Burdekin River at Lake Lucy Dam Site |
S18° 31' E145° 11' |
22 |
2270 |
1973-1994 |
H1, Q |
|
120205 |
Bowen River at Myuna |
S20° 35' E147° 36' |
83 |
7200 |
1960-1990 |
H1, Q |
|
120207 |
Broken River at Urannah |
S20° 55' E148° 19' |
221 |
1100 |
1962-1993 |
H1, Q |
|
120209 |
Bowen River at 89km |
S20° 45' E147° 53' |
116 |
4660 |
1964-1990 |
H1, Q |
|
120214 |
Broken River at Mount Sugarloaf |
S20° 50' E148° 08' |
150 |
2280 |
1969-1993 |
H1, Q |
|
120299 |
Bowen River at Pump Station |
S20° 45' E147° 57' |
118 |
4495 |
1968-1991 |
H1, Q |
|
120301 |
Belyando River at Gregory Dev Rd |
S21° 32' E146° 52' |
172 |
35 530 |
1949-1976 1976-1993 |
H2, Q H1, Q |
|
120302 |
Cape River at Inland Highway |
S21° 00' E146° 26' |
186 |
15 850 |
1948-1968 1968-1994 |
H2, Q H1, Q |
|
120303 |
Suttor River at St Annes |
S21° 14' E146° 55' |
20 |
49 800 |
1948-1967 1967-1994 |
H2, Q H1, Q |
1) H1: water level in recording chart or data logger
H2: water level by manual reading (normally
daily).
Q: discharge
The table below is a list of summary statistics for the selected stations.
|
No. |
[m3/s] |
[m3/s] |
[m3/s] |
[m3/s] |
[m3/s/100km2] |
[m3/s/100km2] |
Cv 5) |
Period of statistics |
||||||||
|
No.120001 |
292 |
40 400 |
10 500 |
0.992 |
0.23 |
31.1 |
0.86 |
1922-1956 |
||||||||
|
120002 |
143 |
23 300 |
6 210 |
0.412 |
0.39 |
64.0 |
1.15 |
1948-1992* |
||||||||
|
120004 |
297 |
29 900 |
9 780 |
0.987 |
0.26 |
26.2 |
1.17 |
1968-1984 |
||||||||
|
120006 |
322 |
36 000 |
11 600 |
0.720 |
0.25 |
27.7 |
1.05 |
1951-1992 |
||||||||
|
120008 |
257 |
39 300 |
8 980 |
2.55 |
0.20 |
31.2 |
1.03 |
1955-1992* |
||||||||
|
120010 |
268 |
26 300 |
8 410 |
1.03 |
0.21 |
20.4 |
1.20 |
1960-1986 |
||||||||
|
120015 |
142 |
13 400 |
4 320 |
0.658 |
0.12 |
11.8 |
0.99 |
1978-1992 |
||||||||
|
120101 |
100 |
25 700 |
5 480 |
0.020 |
0.29 |
73.4 |
0.91 |
1922-1949* |
||||||||
|
120105 |
23.8 |
7 560 |
2 010 |
0 |
0.35 |
112.5 |
0.91 |
1950-1971* |
||||||||
|
120107 |
37.8 |
8 450 |
2 110 |
0.410 |
0.36 |
80.5 |
1.17 |
1953-1987* |
||||||||
|
120110 |
59.7 |
9 600 |
2 970 |
0.387 |
0.34 |
55.1 |
1.25 |
1966-1988 |
||||||||
|
120111 |
21.9 |
3 300 |
1 100 |
0.769 |
0.36 |
53.8 |
1.20 |
1968-1987 |
||||||||
|
120112 |
12.8 |
8 640 |
1 590 |
0 |
1.06 |
717 |
1.06 |
1968-1988 |
||||||||
|
120121 |
12.4 |
1 600 |
474 |
0.004 |
0.55 |
70.5 |
1.29 |
1974-1988 |
||||||||
|
120205 |
24.6 |
15 200 |
2 690 |
0.082 |
0.34 |
211 |
0.93 |
1961-1989 |
||||||||
|
120207 |
10.8 |
3 820 |
1 120 |
0.159 |
0.98 |
347 |
0.87 |
1963-1992* |
||||||||
|
120209 |
21.7 |
12 600 |
2 690 |
0.157 |
0.47 |
270 |
0.94 |
1965-1989 |
||||||||
|
120214 |
21.0 |
9 400 |
2 510 |
0.215 |
0.92 |
412 |
0.90 |
1970-1992* |
||||||||
|
120299 |
29.2 |
5 750 |
2 680 |
0.191 |
0.65 |
128 |
0.80 |
1969-1982 |
||||||||
|
120301 |
28.0 |
2 040 |
698 |
0.008 |
0.08 |
5.74 |
1.05 |
1950-1989* |
||||||||
|
120302 |
26.2 |
2 770 |
1 020 |
0 |
0.17 |
17.5 |
1.18 |
1949-1993* |
||||||||
|
120303 |
57.8 |
10 100 |
1 720 |
0 |
0.12 |
58.0 |
1.15 |
1968-1993 |
||||||||
1) mean annual discharge
2) maximum discharge
3) mean annual maximum discharge
4) mean annual minimum discharge
5) coefficient of variation of annual total discharge
Note: * indicates missing data in some years. These years were excluded from
the statistical analyses.
Details of missing data for each station are; 120002: 1953-54; 120008: 1973-75; 120101: 1923-24 & 1941-48; 120105: 1969-70, 120107: 1982; 120207: 1990-1991; 120214: 1990-91 120301: 1958 & 1969-76; 120302: 1957-68.
4.3 Long-term Variation of Monthly Discharge Series
Graphs of two long term discharge series are shown below:
a) Burdekin River at Home Hill (Station 120001)

b) Burdekin River at Clare (Station 120006)

4.4 Annual Pattern of Discharge Series
Graphs of the discharge series for a selected year and the flow duration curve for the Burdekin River at Clare (Station 120006) are shown below:
a) Discharge series for 1968

b) Flow duration curve

4.5 Unique Hydrological Features
The Australian Institute of Marine Science (AIMS), Townsville is currently involved in the recovery of past hydrological data by utilising the fluorescent properties of coral samples taken from the Great Barrier Reef.
The development of an underwater drilling rig by AIMS has enabled coral core samples of greater than 6 metres in length to be obtained from massive Porites corals. When taken from corals growing within approximately 50 kilometres of the shore, these samples exhibit bands of organic compound (fulvic acid) that are displayed as yellow-green fluorescence when exposed to long-wave ultraviolet light. It is suggested that these bands are the result of decaying plant matter that was deposited on the coral dome by nearby river outlets.
The yellow-green bands occur in the high density sections of the coral skeleton which are usually deposited in the summer or monsoon season. In the more recent coral deposits, fluctuations in the density of these sections have corresponded to documented El Niño episodes. In the western Pacific, El Niño episodes are indicative of dry or poor wet seasons.
AIMS have also developed an analytical instrument that is able to extract fluorescence data with a temporal resolution of 20 days. The process passes 700-800mm long slices of coral 7mm thick through a fluoromicrodensiometer and exposes them to a far ultraviolet (360mm wavelength) source. An ultraviolet light-stable uranyl glass block is used as a calibration standard, and the resultant fluorescence is recorded at 0.5mm intervals along the coral core.
Analysis of the outflow plume from the Burdekin River has shown that the principal plume track is in a northerly direction over the Pandora and Magnetic Island Reefs. However, because the Magnetic Island Reef is also subject to direct runoff from Magnetic Island and the core sample is relatively short, most of the study has concentrated on the Pandora Reef core.
The Queensland Department of Primary Industries, Water Resources, Business Group (formerly the Queensland Water Resourece Commission) has supported AIMS by conducting preliminary and further studies of coral core samples. The fluorescence data obtained has been compared with historical rainfall and streamflow records, namely from the Clare and Home Hill gauging stations, to determine the quality of the relationship. Results to date indicate a high degree of correlation between the two sets of data. Analysis is continuing on establishing the form of a transfer function or model for the estimation of streamflow data from fluorescence data. Future studies will involve the analysis of longer term data sets and the examination of a shorter (monthly) time step.
Coral core sample of 6 metres in length may contain up to 800 years of weather history. Thus, the corals contain a veritable data-bank of Australian hydrological data for many centuries past. The research also has potential application in many of the tropical west Pacific countries where cyclones and destructive floods are a regular summer hazard and long term data on such occurrences are scarce.
4.6 Annual Maximum and Minimum Discharges
The table summarises annual maximum and minimum discharges for the Burdekin River at Clare (Station 120006).
|
Year |
Maximum |
Minimum |
Year |
Maximum |
Minimum |
||||
|
Date |
Discharge [m3/s] |
Month |
Discharge [m3/s] |
Date |
Discharge [m3/s] |
Month |
Discharge [m3/s] |
||
|
1951 |
1.12 |
15 900 |
11/12 |
0 |
1972 |
1.11 |
26 100 |
12 |
0 |
|
1952 |
1.25 |
1 600 |
1/9-11 |
0 |
1973 |
12.20 |
5 800 |
1 |
0 |
|
1953 |
2.15 |
13 300 |
11/12 |
0 |
1974 |
1.23 |
26 600 |
11/12 |
5.14 |
|
1954 |
2.8 |
20 300 |
1 |
0 |
1975 |
1.18 |
6 750 |
9 |
4.95 |
|
1955 |
3.19 |
19 500 |
12 |
0.32 |
1976 |
2.10 |
5 990 |
10 |
1.96 |
|
1956 |
3.9 |
17 700 |
1 |
6.20 |
1977 |
3.11 |
7 110 |
11 |
0.14 |
|
1957 |
1.11 |
2 180 |
12 |
0 |
1978 |
2.1 |
15 300 |
10 |
0.98 |
|
1958 |
4.3 |
36 000 |
1/12 |
0 |
1079 |
3.12 |
12 800 |
12 |
0 |
|
1959 |
2.17 |
19 100 |
10 |
0.29 |
1980 |
1.7 |
9 910 |
11 |
0.39 |
|
1960 |
3.15 |
2 580 |
10/11 |
0 |
1981 |
1.23 |
11 530 |
10 |
1.96 |
|
1961 |
1.6 |
1 950 |
10/11 |
0 |
1982 |
1.28 |
899 |
10 |
0.05 |
|
1962 |
3.10 |
1 470 |
9-11 |
0 |
1983 |
5.2 |
12 400 |
3 |
0.02 |
|
1963 |
4.8 |
5 030 |
12 |
0.18 |
1984 |
2.21 |
3 840 |
10 |
0.27 |
|
1964 |
2.13 |
2 440 |
9 |
0 |
1985 |
3.16 |
1 160 |
10 |
0.11 |
|
1965 |
3.14 |
3 620 |
9-12 |
0 |
1986 |
2.5 |
5 440 |
12 |
1.12 |
|
1966 |
1.29 |
2 700 |
5-9 |
0 |
1987 |
12.31 |
922 |
9 |
2.34 |
|
1967 |
3.11 |
2 460 |
10 |
0 |
1988 |
3.2 |
10 000 |
6 |
1.34 |
|
1968 |
2.17 |
26 000 |
11/12 |
0 |
1989 |
4.5 |
14 900 |
9 |
10.48 |
|
1969 |
12.29 |
515 |
7-12 |
0 |
1990 |
12.28 |
7 560 |
1 |
6.59 |
|
1970 |
1.20 |
17 200 |
9/10 |
0 |
1991 |
2.4 |
29 800 |
7 |
3.39 |
|
1971 |
12.26 |
12 300 |
12 |
0 |
1992 |
12.6 |
672 |
3 |
3.34 |
4.7 Hyetographs and Hydrographs of Major Floods

NOTE: The hydrograph at the Burdekin Dam has not been shown on the figure below. The following information was sourced from Fleming and Loofs, 1991.
During major runoff-producing events, the Burdekin River rarely, if ever, responds as a simple catchment. Most major floods have been generated by the passage of tropical cyclones coupled with local topographic effects, particularly during the heaviest rainfall events. The unpredictable nature of major events in the Burdekin catchment is highlighted by the flood events of January/February 1991.
The Bowen-Broken River system is so placed that it produces topographic enhancement of rainfalls. Further, it is in a naturally high rainfall region and so in most wet seasons has a high level of antecedent wetness (Fleming, et. al., 1981). The hydrograph peak at Clare on January 3rd follows immediately from a hyetograph peak at Collinsville (station 033013) which is located on the lower reaches of the Bowen River. As there was no corresponding hydrograph peak at the dam, most of the streamflow at Clare would have originated from the Bowen-Broken River system. This basin, on its own or in conjunction with other basins, has contributed to a majority of significant flood events (Fleming, et. al., 1981).
Heavy rainfall in the upper Burdekin, as shown by the Greenvale hyetograph, and Cape-Campaspe catchments that started on January 8th and continued for a week resulted in the peak flow at Sellheim on the 13th and a corresponding large steady flow over the dam. As the combined flows at Sellheim and St. Anne's do not add up to the flow over the dam, most of the runoff must have originated from the Cape-Campaspe catchment.
A tropical low triggered high rainfall in the Bowen-Broken catchment on February 2nd. The peak of 29,800m3/s at Clare occurred almost immediately after this. Again, the lack of corresponding peaks in the Burdekin Dam hydrograph suggests that runoff from the Bowen-Broken River catchment was the primary source of this peak. Flows at Sellheim and St. Anne's at about this time indicate that floods in the upper Burdekin and Suttor catchments were quite low. Consequently, the high flows at the dam suggest the significant contribution of the Cape-Campaspe catchment.
During mid-February, a trough lay across the top of the catchment resulting in heavy rainfalls and record river heights upstream of Greenvale (station 032122). The hyetograph at Greenvale indicates this high rainfall immediately preceding the hydrograph peak at Sellheim. This peak would have entered the dam pondage whilst the major Cape-Campaspe flood was still being discharged resulting in the flood peak being transmitted to Clare with little change.
The total flow recorded at Clare during January and February was 33x109m3. Of this, 27x109m3 was discharged over the dam wall, which is 14 times the dam's capacity. About 20x109m3 or 73 percent of the flow into the dam originated from the Upper Burdekin River catchment.
5. Water Resources
5.1 General Description
Most of the streams that feed the Burdekin River are subject to seasonal flows. In many months of the year the availability of water for plant growth is restricted and there is usually insufficient moisture available to attain potential evaporation. The surface water resources are also generally restricted with only 12 percent of the land area yielding about 60 percent of the average annual runoff. Despite the large catchment area, the Burdekin River has ceased to flow on a number of occasions, the longest period being in 1926 and lasting for seven months.
The largest volumes of runoff occur in the eastern highlands where the coastline has a marked north-south orientation which exposes it to the moisture bringing easterly winds. In the lowland of the central coastal region runoff is considerably lower as a result of lower precipitation and generally higher infiltration. One of the most striking features of the runoff is its rapid decrease westwards. This distribution is similar to that of rainfall but more pronounced due to the increase in evaporation. Exceptions to this general tendency are in the western highlands and tablelands where runoff rises slightly due to higher precipitation and lower evaporation, and in the rain shadow area of the middle Burdekin River catchment where the average annual runoff decreases to almost 254mm a year.
There are nine major storages located within the catchment, the largest being Lake Dalrymple created on the Burdekin River as a result of the construction of the Burdekin Falls Dam. This storage has the capacity to provide extensive water supplies to Townsville (just outside the catchment) and the irrigation of existing farms in the lower Burdekin River region. In addition, the dam will be able to supply irrigation to 50 000 hectares of proposed new farmland in the lower area of the catchment. The Burdekin Falls Dam is the largest rural land and water conservation scheme ever undertaken in Queensland. It will also provide water supplies for future urban and industrial development in the major centres of the region well into the next century. The dam has been designed to be raised should plans to construct a hydro-electric power station at the site proceed. This will increase the storage capacity to at least 8.5 x 109 m3. Based on its current capacity, the dam provides an additional 1 x 109 m3 of water each year to the Lower Burdekin catchment area.
Before the completion of this dam, the Burdekin River frequently overtopped its banks in its lower reaches and most of the canelands of the delta and the towns of Home Hill and Ayr were subject to significant flood damage during major floods. Such events usually occurred during the first three months of the year. The Burdekin Falls Dam is designed to reduce the peak flow rates of major floods originating above the Falls by less than 10 percent, but would have no effect on the 30 percent of floods originating below the Falls. It has been recognised that the potential for flood damage in the left bank development area is significant and that the area should be designed and managed in a manner such as to minimise flood damage and ensure the maintenance of the wetland habitats (Fleming, et. al., 1981). Due to the warmer climate and higher wind conditions, moisture supplies are normally exhausted during the winter period. Recently, these losses have been replenished by irrigation.
5.2 Map of Water Resources System

5.3 List of Major Water Resource Facilities
Major Reservoirs
|
Name of river |
Name of dam |
Catchment area [km2] |
Gross capacity [106m3] |
Effective capacity [106m3] |
Purposes |
Year of completion |
|
Swamp Creek |
Paluma Dam |
8 |
12.3 |
12.3 |
W, I |
1958 |
|
Gap Creek |
Gap Creek Dam |
5 |
3.7 |
3.3 |
M |
1993 |
|
Burdekin River |
Charters Towers Weir |
34 980 |
1.9 |
1.8 |
W |
1903 |
|
Burdekin River |
Burdekin Falls Dam |
114 200 |
1860 |
1850 |
A, W, I, F |
1987 |
|
Burdekin River |
Gorge Weir |
115 620 |
7.9 |
7.9 |
A |
1953 |
|
Burdekin River |
Blue Valley Weir |
125 240 |
3.8 |
- |
A |
1963 |
|
Broken River |
Eungella Dam |
142 |
131 |
126 |
A, I |
1969 |
|
Burdekin River |
Clare Weir |
129 435 |
15.5 |
15.2 |
A, W |
1978 |
|
Bowen River |
Bowen River Weir |
4 495 |
2.4 |
1.9 |
M, W |
1983 |
A: Agricultural use, W: Municipal water supply, I: Industrial use, F: Flood control, M: Mining
6. Acknowledgments
The following organisations are thanked for their assistance and advice for the preparation of this work.
ACT Electricity and Water
Australian Bureau of Statistics
Bureau of Meteorology (Canberra, Brisbane and Melbourne offices)
Queensland Department of Primary Industries (Brisbane Mackay and Ayr offices)
General Reference Maps of Australia are reproduced with the permission of General Manager , Australian Surveying and Land Information Group (AUSLIG). Department of Administrative Services, Canberra.
In addition, Mr Mick Fleming, formerly of the Division of Water Resources, CSIRO is thanked for providing useful reference material and helpful comments.
7. References, Databooks and Bibliography
BURDEKIN PROJECT COMMITTEE, 1977. Resources and Potential of the Burdekin River Basin, Queensland. Australian Government Publishing Service. 195pp.
DEPARTMENT OF MINERALS AND ENERGY, DIVISION OF NATIONAL MAPPING, GEOGRAPHIC SECTION, 1973. Burdekin - Townsville Region Queensland Resources Series. pp 1-35.
DEPARTMENT OF RESOURCES AND ENERGY and Australian Water Resources Council, 1984. Stream Gauging Information, Australia. Australian Government Publishing Service. 204pp.
FLEMING P.M., and LOOFS M., 1991 Flood Generation and Transmission in the Burdekin and Haughton Rivers North Queensland. CSIRO Division of Water Resources Technical Memorandum 91/15
FLEMING P.M., GUNN R.H., REECE A.M., and McALPINE J.R., 1981. Burdekin Project Ecological Study. Australian Government Publishing Service. 222pp.
ISDALE P.J., STEWART B.J., and TICKLE K.S., 1986. Weather Records in Corals. Proceedings of the IEAust Hydrology and Water Resources Symposium, Brisbane, NCP 86/13, pp376-377.
ISDALE P., STEWART B., and TICKLE K., 1989. Reconstruction of Past Hydrological Data in the Burdekin River Basin. Proceedings of the IEAust Hydrology and Water Resources Symposium, Christchurch, NCP 89/19, p156-160.
QUEENSLAND Department of Primary Industries - Water Resources Brochure - Water the Essence of Life Burdekin Irrigation Project. 4pp.
QUEENSLAND Department of Primary Industries, 1991. Three Day Isohyets for 1991 Event, Internal Report.
QUEENSLAND Department of primary industries, 1994. Overview of Water Resources and Related Issues: The Upper Burdekin Region. 35pp.
QUEENSLAND WATER RESOURCES COMMISSION, 1980. Report on Establishment of Burdekin River Project Undertaking. 191pp.
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