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Indices
Legend
The charts show the distribution of the site scores for the catchment in a box and whisker
plot. The image to the right shows the meaning of the different elements in the chart.
The number behind the charts is the number of sites with valid data. It can be less
than the total number of sites in the catchment if some data could not be collected.
A description of the indicators and methods used can be downloaded as a PDF file.
Summary
Eighteen sites were assessed in the Upper Brisbane reporting area, which was awarded a 2009 Report Card grade of ‘D+’,
higher than its 2008 grade of ‘D‑’. Streams were generally in poor condition. The grade for this reporting area has
improved over the past three years, but the Fish indicator still scores poorly.
The three highest scoring indices for the Upper Brisbane reporting area during 2008‑09 were pH (Annual Reporting Area
Index Score = 1.00), Number of Taxa (0.91) and δ15N (0.88). The three lowest scoring indices for the area
were O/E50 (0.54), Proportion Alien (0.56) and PONSE (0.62).
The assessment site yielding the highest annual score (indicating the best ecological condition) during 2008‑09 was one
on Sandy Creek (site 143‑0020) with a very good score of 0.89. The assessment site yielding the lowest annual score
(indicating the worst ecological condition) during 2008‑09 was one on Esk Creek (site 143‑0018) with a fair score of
0.61. This site is situated a short distance upstream of the impounded waters of Lake Wivenhoe, and much of the land in
the associated upper catchment has been heavily cleared for agriculture.
Abbreviations glossary
Site scores
| Spring Site Indicator Scores |
| Site Code |
Physical and Chemical |
Nutrient Cycling |
Ecosystem Processes |
Aquatic Macroinvertebrates |
Fish |
| 143-0001 |
0.58 |
1.00 |
0.77 |
0.73 |
- |
| 143-0003 |
0.69 |
0.52 |
0.78 |
0.59 |
- |
| 143-0004 |
0.46 |
1.00 |
0.86 |
0.76 |
0.28 |
| 143-0006 |
0.82 |
1.00 |
0.97 |
0.96 |
0.05 |
| 143-0008 |
0.89 |
1.00 |
0.98 |
0.80 |
0.68 |
| 143-0009 |
0.94 |
- |
0.75 |
0.91 |
0.38 |
| 143-0010 |
0.90 |
1.00 |
0.69 |
0.89 |
0.66 |
| 143-0011 |
0.93 |
1.00 |
0.49 |
0.87 |
0.65 |
| 143-0012 |
0.61 |
1.00 |
0.95 |
0.74 |
0.68 |
| 143-0013 |
0.85 |
0.86 |
0.83 |
0.80 |
0.41 |
| 143-0014 |
0.72 |
1.00 |
0.60 |
0.44 |
0.40 |
| 143-0015 |
0.50 |
1.00 |
0.85 |
0.78 |
0.60 |
| 143-0016 |
0.87 |
- |
0.40 |
0.80 |
0.71 |
| 143-0017 |
0.86 |
1.00 |
0.42 |
0.88 |
0.94 |
| 143-0018 |
0.55 |
0.00 |
1.00 |
0.97 |
0.36 |
| 143-0020 |
0.88 |
0.92 |
0.87 |
0.86 |
0.68 |
| 143-0021 |
0.70 |
1.00 |
0.17 |
0.82 |
0.54 |
| 143-0060 |
0.75 |
0.06 |
1.00 |
0.49 |
- |
| Autumn Site Indicator Scores |
| Site Code |
Physical and Chemical |
Nutrient Cycling |
Ecosystem Processes |
Aquatic Macroinvertebrates |
Fish |
| 143-0001 |
0.75 |
- |
- |
0.69 |
- |
| 143-0003 |
0.77 |
- |
0.90 |
0.83 |
0.45 |
| 143-0004 |
0.79 |
1.00 |
0.76 |
0.74 |
0.29 |
| 143-0006 |
0.90 |
1.00 |
0.98 |
0.92 |
0.12 |
| 143-0008 |
0.81 |
1.00 |
0.56 |
0.85 |
0.53 |
| 143-0009 |
0.95 |
- |
0.46 |
0.79 |
0.39 |
| 143-0010 |
0.90 |
1.00 |
0.67 |
0.92 |
0.82 |
| 143-0011 |
0.75 |
1.00 |
0.86 |
0.90 |
0.69 |
| 143-0012 |
0.67 |
1.00 |
0.67 |
0.77 |
0.64 |
| 143-0013 |
0.85 |
1.00 |
0.79 |
0.73 |
0.49 |
| 143-0014 |
0.69 |
1.00 |
0.50 |
0.68 |
0.49 |
| 143-0015 |
0.70 |
1.00 |
0.65 |
0.71 |
0.54 |
| 143-0016 |
0.78 |
0.84 |
0.45 |
- |
0.58 |
| 143-0017 |
0.72 |
1.00 |
0.79 |
0.95 |
0.89 |
| 143-0018 |
0.95 |
0.00 |
1.00 |
0.74 |
0.53 |
| 143-0020 |
0.94 |
1.00 |
0.84 |
0.99 |
0.91 |
| 143-0021 |
1.00 |
1.00 |
0.93 |
0.92 |
0.61 |
| 143-0060 |
0.73 |
1.00 |
0.79 |
0.73 |
0.75 |
| Annual Site Indicator Scores |
| Site Code |
Physical and Chemical |
Nutrient Cycling |
Ecosystem Processes |
Aquatic Macroinvertebrates |
Fish |
| 143-0001 |
0.66 |
1.00 |
0.77 |
0.71 |
- |
| 143-0003 |
0.73 |
0.52 |
0.84 |
0.71 |
0.45 |
| 143-0004 |
0.63 |
1.00 |
0.81 |
0.75 |
0.29 |
| 143-0006 |
0.86 |
1.00 |
0.97 |
0.94 |
0.09 |
| 143-0008 |
0.85 |
1.00 |
0.77 |
0.82 |
0.60 |
| 143-0009 |
0.94 |
- |
0.61 |
0.85 |
0.38 |
| 143-0010 |
0.90 |
1.00 |
0.68 |
0.91 |
0.74 |
| 143-0011 |
0.84 |
1.00 |
0.67 |
0.89 |
0.67 |
| 143-0012 |
0.64 |
1.00 |
0.81 |
0.76 |
0.66 |
| 143-0013 |
0.85 |
0.93 |
0.81 |
0.77 |
0.45 |
| 143-0014 |
0.71 |
1.00 |
0.55 |
0.56 |
0.45 |
| 143-0015 |
0.60 |
1.00 |
0.75 |
0.75 |
0.57 |
| 143-0016 |
0.83 |
0.84 |
0.43 |
0.80 |
0.65 |
| 143-0017 |
0.79 |
1.00 |
0.60 |
0.92 |
0.92 |
| 143-0018 |
0.75 |
0.00 |
1.00 |
0.86 |
0.45 |
| 143-0020 |
0.91 |
0.96 |
0.85 |
0.92 |
0.79 |
| 143-0021 |
0.85 |
1.00 |
0.55 |
0.87 |
0.58 |
| 143-0060 |
0.74 |
0.53 |
0.89 |
0.61 |
0.75 |
The scores range from 0.0 (worst) to 1.0 (best). A dash ('-') indicates that sufficient data
was not available.
Flowchart for calculation of summary statistics based on site scores
Map
| Site Code |
Waterway |
|
Site Name |
| 143-0001 |
Yarraman Creek |
|
Din Din Road, Yarraman |
| 143-0003 |
Pierces Creek |
|
Pierces Creek Road, Pierces Creek |
| 143-0004 |
Emu Creek |
|
Pierces Creek Road, Sylvia Vale |
| 143-0006 |
Crows Nest Creek |
|
Crows Nest National Park, Crows Nest - Esk Road |
| 143-0008 |
Brisbane River (West Branch) |
|
Linville - Murgon Road, Avoca Vale |
| 143-0009 |
Brisbane River (East Branch) |
|
Eastern Branch Road, Mount Stanley |
| 143-0010 |
Kangaroo Creek |
|
Kangaroo Creek Road, Boomerang Gap |
| 143-0011 |
Monsildale Creek |
|
Monsildale Creek Road, Mount Pascoe |
| 143-0012 |
Emu Creek |
|
via Grieves Road, Harlin |
| 143-0013 |
Wallaby Creek |
|
Himstedts Road, Moore |
| 143-0014 |
Maronghi Creek |
|
Maronghi Creek Road, Harlin |
| 143-0015 |
Ivory Creek |
|
Ivory Creek Road, Ivory Creek |
| 143-0016 |
Cressbrook Creek |
|
Esk - Crows Nest Road, Noonans Corner |
| 143-0017 |
Brisbane River |
|
Arababy Creek Road, The Round Mountain |
| 143-0018 |
Esk Creek |
|
Falls Road, Esk |
| 143-0020 |
Sandy Creek |
|
Wivenhoe - Somerset Road, Crossdale |
| 143-0021 |
Northbrook Creek |
|
Northbrook Parkway, Dundas |
| 143-0060 |
Cooyar Creek |
|
Kooralgin - Gilla Road, Pidna State Forest |
Facts
- Total area: 5,493km²
- Stream network length: 11,368km
- Local Councils: Toowoomba Regional Council, Somerset Regional
Council
- Dominant land uses: native bush, grazing, intensive
agriculture, waterbodies
- The upper catchment is located in the foothills of the Great
Dividing Range and the Conondale Range, remaining in a relatively
natural state
- The majority of the remaining catchment has been cleared for
grazing and rural residential use, with limited riparian vegetation
present
- The upper Brisbane River is impounded by Wivenhoe Dam, which
acts as an effective trap for sediment from the upper catchment
Fish
Fish species identified in Upper Brisbane streams
| Species |
Common name |
| Ambassis agassizii |
Olive perchlet |
| Amniataba percoides |
Barred grunter [T] |
| Anguilla reinhardtii |
Long-finned eel |
| Carassius auratus |
Goldfish [A] |
| Craterocephalus marjoriae |
Marjorie's hardyhead |
| Craterocephalus stercusmuscarum |
Fly-specked hardyhead |
| Gambusia holbrooki |
Gambusia [A] |
| Glossamia aprion |
Mouth almighty |
| Hypseleotris galii |
Fire-tail gudgeon |
| Hypseleotris klunzingeri |
Western carp gudgeon |
| Leiopotherapon unicolor |
Spangled perch |
| Macquaria ambigua |
Golden perch [T] |
| Macquaria novemaculeata |
Australian bass |
| Melanotaenia duboulayi |
Duboulay's rainbowfish |
| Mogurnda adspersa |
Southern purple-spotted gudgeon |
| Oreochromis mossambicus |
Mozambique mouthbrooder [A] |
| Philypnodon grandiceps |
Flathead gudgeon |
| Philypnodon macrostomus |
Dwarf flathead gudgeon |
| Retropinna semoni |
Australian smelt |
| Tandanus tandanus |
Eel-tailed catfish |
| [A] | Alien species |
| [T] | Translocated species |
| [EM] | Estuarine-Marine species |
Macroinvertebrates
Aquatic macroinvertebrate taxa identified in Upper Brisbane freshwater streams
| Class |
Order |
Taxa |
| Arachnida |
s.o. Acariformes |
Acarina |
| |
Araneae |
Araneae |
| Bivalvia |
Veneroida |
Corbiculidae |
| |
|
Sphaeriidae |
| Branchiopoda |
Cladocera |
Cladocera |
| Copepoda |
– |
Copepoda |
| Gastropoda |
Basommatophora |
Ancylidae |
| |
|
Lymnaeidae |
| |
|
Physidae |
| |
|
Planorbidae |
| |
Mesogastropoda |
Hydrobiidae |
| |
|
Thiaridae |
| s.c. Hirudinea |
– |
Glossiphoniidae |
| Insecta |
s.o. Anisoptera |
Cordulephyidae |
| |
|
Gomphidae |
| |
|
Hemicorduliidae |
| |
|
Libellulidae |
| |
|
Lindeniidae |
| |
|
Synthemistidae |
| |
|
Telephlebiidae |
| |
Coleoptera |
Curculionidae |
| |
|
Dytiscidae |
| |
|
Elmidae |
| |
|
Gyrinidae |
| |
|
Haliplidae |
| |
|
Hydraenidae |
| |
|
Hydrochidae |
| |
|
Hydrophilidae |
| |
|
Noteridae |
| |
|
Psephenidae |
| |
|
Scirtidae |
| |
|
Staphylinidae |
| |
Collembola |
Collembola |
| |
Diptera |
Ceratopogonidae |
| |
|
Culicidae |
| |
|
Empididae |
| |
|
Ephydridae |
| |
|
s.f. Chironominae |
| |
|
s.f. Orthocladiinae |
| |
|
s.f. Tanypodinae |
| |
|
Stratiomyidae |
| |
|
Syrphidae |
| |
|
Tabanidae |
| |
Ephemeroptera |
Baetidae |
| |
|
Caenidae |
| |
|
Leptophlebiidae |
| |
Hemiptera |
Belostomatidae |
| |
|
Corixidae |
| |
|
Gelastocoridae |
| |
|
Gerridae |
| |
|
Hebridae |
| |
|
Hydrometridae |
| |
|
Mesoveliidae |
| |
|
Naucoridae |
| |
|
Nepidae |
| |
|
Notonectidae |
| |
|
Pleidae |
| |
|
Veliidae |
| |
Lepidoptera |
Pyralidae |
| |
Megaloptera |
Sialidae |
| |
Neuroptera |
Sisyridae |
| |
Trichoptera |
Calamoceratidae |
| |
|
Ecnomidae |
| |
|
Hydroptilidae |
| |
|
Leptoceridae |
| |
|
Philopotamidae |
| |
s.o. Zygoptera |
Coenagrionidae |
| |
|
Isostictidae |
| |
|
Megapodagrionidae |
| |
|
Protoneuridae |
| Malacostraca |
Amphipoda |
Talitridae |
| |
Decapoda |
Atyidae |
| |
|
Palaemonidae |
| |
|
Parastacidae |
| |
Isopoda |
Cirolanidae |
| phy. Nematoda |
– |
Nematoda |
| s.c. Oligochaeta |
– |
Oligochaeta |
| Ostracoda |
– |
Ostracoda |
| Turbellaria |
Seriata |
Dugesiidae |
|