Modelling dry season flows and predicting the impact of water extraction of flagship species
Georges, Aurthur; Webster, Ian; Guarino, Fiorenzo; Jolly, Peter; Thoms, Martin; Doody, Sean; CRC for Freshwater Ecology (Australia); University of Canberra. Applied Ecology Research Group
E-Publications; E-Books; PublicationNT; 57/2002; National River health program
2002-11-20
Daly River
The aim of this project is to contribute to recommendations on environmental flows to ensure that they are consistent with maintaining the biota of the Daly River, given competing demands of agriculture, recreation and tourism, conservation and Aboriginal culture. Our focus is on flow, connectivity and water temperatures.
Made available by via Publications (Legal Deposit) Act 2004 (NT); Submitted to the Northern Territory. Department of Infrastructure Planning and Environment
1. Project Details -- 2. Executive Summary -- 3. Interpretation of the Brief -- 4. Variation of the Brief -- 5. Background -- 6. The Daly Drainage -- 7. The Pig-nosed turtle -- 8. Analysis of Historical Flow Data -- 9. Analysis of Contemporary Flow Data -- 10. Modelling Flow Reduction -- 11. Water Temperature Versus Flow -- 12. Impact on Flagship Species -- 13. References
English
Environmental Flows; Modelling; Biota
Northern Territory Government
Palmerston
Final Report
57/2002; National River health program
75 pages ; 30 cm
application/pdf
Attribution International 4.0 (CC BY 4.0)
Northern Territory Government
https://creativecommons.org/licenses/by/4.0/
https://hdl.handle.net/10070/885434
https://hdl.handle.net/10070/885435
39 80% Reduction (4.8 cumecs) When 4.8 cumecs of flow entering at Dorisvale Crossing, 20 breaks occur in the Daly River between Dorisvale Crossing and Cattle Creek (Table 8). This translates into one break point for every 3.68 km of river. Table 8. Location of breakpoints on the Daly River under modelled flow conditions. Upstream flow was 4.8 cumecs at Dorisvale Crossing and downstream flow was 8.5 cumecs at Cattle Creek. Breakpoints refer to sections of the river that would inhibit movement of pig-nosed turtles (<0.5 m). Landmark Distance (km) Easting Northing Pool length (km) Cp1 Dorisvale 0.00 775734 8410582 0.00 Cp3 9.16 770965 8415100 9.16 Cp4 11.17 769734 8416517 2.01 Cp5 13.20 767888 8416689 2.03 Riffle 16.54 765700 8418696 3.34 Riffle 18.29 764677 8420100 1.75 Cp10 H springs 24.39 761242 8423735 6.11 Cp12 25.96 760962 8424597 1.56 Cp13 31.12 760673 8429515 5.16 Cp14 32.33 759623 8429728 1.21 Cp15 B B yard 33.38 758756 8430438 1.05 Cp17 43.62 751885 8433540 10.25 Cp18 44.87 750816 8432984 1.24 Cp19 46.67 749665 8431792 1.80 Cp20 48.62 749081 8433494 1.95 Cp21 53.16 748556 8437714 4.54 Cp22 54.17 747717 8437410 1.01 Cp23 Jinduckin 55.91 746875 8437186 1.74 Cp25 Oolloo Xing 66.98 743191 8443228 11.07 Cp26 Cattle ck 73.27 738867 8445392 6.29 Under this flow regime (4.8 cumecs), the 20 break points identified above produce 19 pools in the Daly River, between Dorisvale Crossing and Cattle Creek. Notably there were no very large pools. There were 11 small pools (58%), 5 intermediate pools (26%) and 3 large pools (16%) (Figures 21 & 22). Under these flow conditions, 23.5% (17.3 km) of the study reach would be fragmented into small pools, 34.5% (25.4 km) would be fragmented into intermediate pools and 41.4% (30.5 km) would be fragmented into large pools.