1.5.2.1 Surface water


Queensland has a surface water quality network of about 240 stations monitoring in situ measurements using manual sampling as well as continuous water quality measurements (167 stations). These measurements generally include electrical conductivity (EC) at 25 °C, temperature, pH, turbidity, nutrients, dissolved oxygen and total alkalinity (DERM, 2012). The manual water sampling frequency for all stations in the subregion is four times a year, except in the Oakey Creek (tributary of the Condamine River), which is sampled 12 times a year (DERM, 2012). The water quality in the three river basins are described in the following sections.

1.5.2.1.1 Water quality in the Condamine-Balonne river basin

Water quality data were collected in the Condamine-Balonne river basin (Figure 4) for a range of water quality markers including total nitrogen, total phosphorus, total suspended solids and many other chemicals, such as cadmium, copper, the herbicides Atrazine and Diuron, and the insecticide Dieldrin (DERM, 2011). In the upper Condamine river basin, nutrient levels were generally within the guidelines at the nutrient monitoring sites as described in DERM (2011). In addition, an ambient surface water quality summary report by the Department of Environment and Resource Management only reports the direction of water quality trends (mostly improving trends) due to data limitations in most Queensland river basins. They note that reporting on magnitude would not be sufficiently reliable or meaningful (DERM, 2011).

The 20 stations with EC data in the Condamine-Balonne river basin are shown in Table 7. Two examples of EC data in the Condamine-Balonne river basin are shown in Figure 11 and Figure 12 for the period from 1995 to 2015. The data gap shows when data were not collected. This was primarily due to no flow conditions and sometimes due to monitoring equipment failure. EC measured at the Condamine River at Chinchilla (422308C) station ranged from 77 to 1094 µS/cm with a mean of 447 µS/cm. The highest EC values occurred during low flows, which is more saline than in many other rivers in Queensland. EC measured near the outlet of the Condamine-Balonne river basin at the Culgoa River at Whyenbah (422204A) varies between 53 and 584 µS/cm with a mean of 187 µS/cm.

Figure 11

Figure 11 Observed electrical conductivity at gauging station 422204A, Culgoa River at Whyenbah

Data: Queensland Department of Natural Resources and Mines (Dataset 1)

Figure 12

Figure 12 Observed electrical conductivity at gauging station 422308C, Condamine River at Chinchilla Weir

Data: Queensland Department of Natural Resources and Mines (Dataset 1)

Table 7 Gauging stations and monitoring period for electrical conductivity in the Condamine-Balonne river basin


Station number

Station name and location

Catchment area (km2)

Start date

End date

422204A

Culgoa River at Whyenbah

79,330

02 Mar 1995

24 Feb 2015

422207A

Ballandool River at Hebel Bollon Road

80,185

15 May 2002

04 Mar 2015

422209A

Bokhara River at Hebel

80,030

16 May 2002

13 May 2015

422211A

Briarie Creek at Woolerbilla-Hebel Road

410

15 May 2002

24 Feb 2015

422306A

Swan Creek at Swanfels

83

10 Feb 1993

13 May 2015

422308C

Condamine River at Chinchilla Weir

19,190

25 Jul 1995

13 May 2015

422310C

Condamine River at Warwick

1,360

12 Feb 1993

21 Jan 2015

422313B

Emu Creek at Emu Vale

148

10 Feb 1993

13 May 2015

422316A

Condamine River at Cecil Weir

7,795

17 Feb 1993

29 Sep 2014

422319B

Dalrymple Creek at Allora

246

09 Feb 1993

20 Jan 2015

422323A

Condamine River at Tummaville

6,475

25 Feb 1993

30 Sep 2014

422326A

Gowrie Creek at Cranley

47

03 Mar 1993

31 Jul 2014

422332B

Gowrie Creek at Oakey

142

06 Jan 1994

26 Feb 2015

422333A

Condamine River at Loudouns Bridge

12,380

11 Feb 1993

25 Sep 2014

422334A

Kings Creek at Aides Bridge

516

17 Feb 1993

01 Oct 2014

422338A

Canal Creek at Leyburn

395

17 Feb 1993

14 Nov 2014

422345A

North Condamine River at Lone Pine

710

27 Apr 1993

29 Sep 2014

422350A

Oakey Creek at Fairview

1,970

11 Feb 1993

25 Feb 2015

422352A

Hodgson Creek at Balgownie

560

09 Feb 1993

01 Oct 2014

422394A

Condamine River at Elbow Valley

325

10 Feb 1993

09 Feb 2015

Data: Queensland Government (2015)

1.5.2.1.2 Water quality in the Moonie river basin

The two stations in the Moonie River at Nindigully (417201B) and at Fenton (417204A) as shown in Figure 5 have high concentrations of total nitrogen, which requires management action (DERM, 2011). EC data was only available from the station at the Moonie River at Fenton (417204A) for the period from 2003 to 2015, as shown in Table 8 and Figure 13. The data gap shows when data were not collected. This was primarily due to no flow conditions and sometimes due to monitoring equipment failure. EC measured at the Moonie River at Fenton (417204A) station ranged from 6 to 395 µS/cm with a mean of 143 µS/cm.

Table 8 Gauging stations and monitoring period for electrical conductivity in the Moonie river basin


Station number

Station name and location

Catchment area (km2)

Start date

End date

417201B

Moonie River at Nindigully

12,030

NA

NA

417204A

Moonie River at Fenton

14,050

13 Jan 2003

23 Feb 2015

Data: Queensland Government (2015) NA means data not available

Figure 13

Figure 13 Observed electrical conductivity at gauging station 417204A, Moonie River at Fenton

Data: Queensland Department of Natural Resources and Mines (Dataset 1)

1.5.2.1.3 Water quality in the Border Rivers river basin

Sites in the Border Rivers river basin (Figure 6) in Queensland are monitored on a monthly basis by the NSW Office of Water on behalf of the Dumaresq Barwon Border Rivers Commission for EC, nutrients, turbidity, total suspended solids and water temperature. Summary statistics are reported for EC, total phosphorus, total nitrogen and turbidity (DBBRC, 2012a). Median salinity in the Border Rivers river basin is below the low salinity guidelines (300 µS/cm) for irrigation water (DBBRC, 2012b). However, Macintyre Brook had salinity levels above the guidelines (350 µS/cm) for protection of aquatic ecosystems in upland streams. Turbidity levels in the Border Rivers river basin showed a gradual increase downstream along the waterway towards Mungindi (DBBRC, 2012b).

Four stations in the Border Rivers river basin had EC data (Table 9). Figure 14 shows an example of auto-sensor EC data in the Border Rivers river basin (station 416202A, Weir River at Talwood) for the period from 2002 to 2015. The data gap shows when data were not collected, especially between 2006 and 2008. This was primarily due to no flow conditions and sometimes due to monitoring equipment failure. EC measured at the Weir River at Talwood (416202A) station ranged from 29 to 471 µS/cm with a mean of 171 µS/cm. DERM (2011) however reports that the streamflow gauging station in the Weir River has insufficient water quality data to assess levels and trends of EC, nitrogen, phosphorus and turbidity. In Macintyre Brook, EC is within the guidelines, whereas data for nitrogen, phosphorus and turbidity are insufficient for meaningful assessment (DERM, 2011).

Table 9 Gauging stations and monitoring period for electrical conductivity in the Border Rivers river basin


Station number

Station name and location

Catchment area (km2)

Start date

End date

416202A

Weir River at Talwood

12,070

29 Aug 2002

26 Feb 2015

416310A

Dumaresq River at Farnbro

1,310

12 Mar 2002

03 Mar 2015

416317A

Broadwater Creek at Barkers

108

21 Mar 1994

18 Feb 2015

416415A

Macintyre Brook at Booba Sands

4,092

30 May 2002

13 Nov 2014

Data: Queensland Government (2015)

Figure 14

Figure 14 Observed electrical conductivity at the gauging station 416202A, Weir River at Talwood

Data: Queensland Department of Natural Resources and Mines (Dataset 1)

1.5.2.1.4 Gaps

There is a lack of long-term consistent water quality data measurements including EC at 25 °C, water temperature, turbidity, and nutrients within the Maranoa-Balonne-Condamine subregion, especially for the Moonie River and Border Rivers. As a result, the capacity to fully understand the baseline water quality for this area is limited.

Last updated:
5 January 2018