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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
Nine sites were assessed in the Bremer 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 and increases in Ecosystem Processes, Aquatic
Macroinvertebrate and Fish indicators contributed to the increase in grade.
The three highest scoring indices for the Bremer reporting area during 2008‑09 were pH (Annual Reporting Area Index
Score = 1.00), GPP (0.98) and δ13C (0.92). The three lowest scoring indices for the area were
O/E50 (0.59), Temperature (0.62) and δ15N (0.63).
The assessment site yielding the highest annual score (indicating the best ecological condition) during 2008‑09 was one
on Warrill Creek (site 143‑0044) with an excellent score of 0.93. The assessment site yielding the lowest annual score
(indicating the worst ecological condition) during 2008‑09 was one on Western Creek (site 143‑0048) with a poor score of
0.59. This site is located within a substantial agricultural area and upstream reaches of the associated stream have
little riparian vegetation.
Abbreviations glossary
Site scores
| Spring Site Indicator Scores |
| Site Code |
Physical and Chemical |
Nutrient Cycling |
Ecosystem Processes |
Aquatic Macroinvertebrates |
Fish |
| 143-0044 |
0.69 |
0.98 |
0.84 |
1.00 |
1.00 |
| 143-0045 |
0.88 |
- |
1.00 |
0.94 |
0.91 |
| 143-0046 |
0.46 |
- |
- |
0.51 |
0.64 |
| 143-0048 |
0.47 |
- |
- |
0.54 |
0.54 |
| 143-0049 |
0.75 |
0.48 |
0.86 |
0.96 |
0.58 |
| 143-0051 |
0.63 |
- |
- |
0.66 |
0.22 |
| 143-0052 |
0.61 |
0.94 |
0.91 |
0.86 |
0.59 |
| 143-0053 |
0.58 |
0.82 |
1.00 |
0.65 |
- |
| 143-0064 |
0.70 |
- |
- |
0.81 |
0.65 |
| Autumn Site Indicator Scores |
| Site Code |
Physical and Chemical |
Nutrient Cycling |
Ecosystem Processes |
Aquatic Macroinvertebrates |
Fish |
| 143-0044 |
0.94 |
1.00 |
0.95 |
0.93 |
1.00 |
| 143-0045 |
0.95 |
0.00 |
1.00 |
0.94 |
0.94 |
| 143-0046 |
0.96 |
- |
0.90 |
0.76 |
0.55 |
| 143-0048 |
1.00 |
- |
- |
0.55 |
0.42 |
| 143-0049 |
0.98 |
0.37 |
0.87 |
0.96 |
0.88 |
| 143-0051 |
0.87 |
- |
1.00 |
0.30 |
0.59 |
| 143-0052 |
0.71 |
- |
- |
0.75 |
0.68 |
| 143-0053 |
0.72 |
- |
- |
0.50 |
0.57 |
| 143-0064 |
0.95 |
- |
- |
0.85 |
0.86 |
| Annual Site Indicator Scores |
| Site Code |
Physical and Chemical |
Nutrient Cycling |
Ecosystem Processes |
Aquatic Macroinvertebrates |
Fish |
| 143-0044 |
0.81 |
0.99 |
0.90 |
0.97 |
1.00 |
| 143-0045 |
0.91 |
0.00 |
1.00 |
0.94 |
0.92 |
| 143-0046 |
0.71 |
- |
0.90 |
0.63 |
0.60 |
| 143-0048 |
0.73 |
- |
- |
0.55 |
0.48 |
| 143-0049 |
0.87 |
0.43 |
0.86 |
0.96 |
0.73 |
| 143-0051 |
0.75 |
- |
1.00 |
0.48 |
0.41 |
| 143-0052 |
0.66 |
0.94 |
0.91 |
0.80 |
0.63 |
| 143-0053 |
0.65 |
0.82 |
1.00 |
0.58 |
0.57 |
| 143-0064 |
0.83 |
- |
- |
0.83 |
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 |
| 143-0044 |
Warrill Creek |
|
Villis Bridge, Neibling Road, Tarome |
| 143-0045 |
Reynolds Creek |
|
Gorge Road, Charlwood |
| 143-0046 |
Bremer River |
|
Adams Bridge, Rosewood - Aratula Road, Rosevale |
| 143-0048 |
Western Creek |
|
Bakers Road, Grandchester |
| 143-0049 |
Warrill Creek |
|
Kalbar Connection Road, Kalbar |
| 143-0051 |
Bundamba Creek |
|
George Palmer Park, Sealy Street, Silkstone |
| 143-0052 |
Purga Creek |
|
Ipswich - Boonah Road, Peak Crossing |
| 143-0053 |
Purga Creek |
|
Purga School Road, Purga |
| 143-0064 |
Bremer River |
|
Haigslea - Amberley Road, Walloon |
Facts
- Total area: 2,031km²
- Stream network length: 4,425km
- Local Councils: Ipswich City Council, Scenic Rim Council
- Dominant land uses: grazing, native bush, intensive
agriculture, urban
- Lower catchment mostly urbanised, rest of the catchment
rural, with the majority of the catchment cleared for cattle grazing
- Some areas of natural bush remaining in upper catchment
- Widespread channel and gully erosion in the river and its
tributaries
- Riparian vegetation significantly modified; little native
vegetation remaining
- Four WWTPs and other point sources discharging into the
catchment’s waterways, contributing to sediment and nutrient loads
Fish
Fish species identified in Bremer streams
| Species |
Common name |
| Ambassis agassizii |
Olive perchlet |
| Anguilla australis |
Short-finned eel |
| Anguilla reinhardtii |
Long-finned eel |
| Carassius auratus |
Goldfish [A] |
| Craterocephalus marjoriae |
Marjorie's hardyhead |
| Craterocephalus stercusmuscarum |
Fly-specked hardyhead |
| Gambusia holbrooki |
Gambusia [A] |
| Hypseleotris compressa |
Empire gudgeon |
| Hypseleotris galii |
Fire-tail gudgeon |
| Hypseleotris klunzingeri |
Western carp gudgeon |
| Leiopotherapon unicolor |
Spangled perch |
| Melanotaenia duboulayi |
Duboulay's rainbowfish |
| Mogurnda adspersa |
Southern purple-spotted gudgeon |
| Mugil cephalus |
Sea mullet |
| Nematalosa erebi |
Bony bream |
| Philypnodon grandiceps |
Flathead gudgeon |
| Pseudomugil signifer |
Southern blue-eye |
| Retropinna semoni |
Australian smelt |
| Tandanus tandanus |
Eel-tailed catfish |
| Xiphophorus maculatus |
Platy [A] |
| [A] | Alien species |
| [T] | Translocated species |
| [EM] | Estuarine-Marine species |
Macroinvertebrates
Aquatic macroinvertebrate taxa identified in Bremer freshwater streams
| Class |
Order |
Taxa |
| Arachnida |
s.o. Acariformes |
Acarina |
| |
Araneae |
Araneae |
| Bivalvia |
s.c. Paleoheterodonta |
Hyriidae |
| |
Veneroida |
Sphaeriidae |
| Branchiopoda |
Cladocera |
Cladocera |
| Copepoda |
– |
Copepoda |
| Gastropoda |
Basommatophora |
Ancylidae |
| |
|
Lymnaeidae |
| |
|
Physidae |
| |
|
Planorbidae |
| |
Mesogastropoda |
Hydrobiidae |
| s.c. Hirudinea |
– |
Glossiphoniidae |
| |
|
Hirudinidae |
| Hydrozoa |
Hydroida |
Hydridae |
| Insecta |
s.o. Anisoptera |
Gomphidae |
| |
|
Hemicorduliidae |
| |
|
Libellulidae |
| |
Coleoptera |
Curculionidae |
| |
|
Dytiscidae |
| |
|
Gyrinidae |
| |
|
Haliplidae |
| |
|
Hydraenidae |
| |
|
Hydrochidae |
| |
|
Hydrophilidae |
| |
|
Noteridae |
| |
|
Psephenidae |
| |
|
Scirtidae |
| |
Collembola |
Collembola |
| |
Diptera |
Ceratopogonidae |
| |
|
Culicidae |
| |
|
Dixidae |
| |
|
s.f. Chironominae |
| |
|
s.f. Orthocladiinae |
| |
|
s.f. Tanypodinae |
| |
|
Simuliidae |
| |
|
Stratiomyidae |
| |
|
Tabanidae |
| |
|
Tipulidae |
| |
Ephemeroptera |
Baetidae |
| |
|
Caenidae |
| |
|
Leptophlebiidae |
| |
Hemiptera |
Belostomatidae |
| |
|
Corixidae |
| |
|
Gelastocoridae |
| |
|
Gerridae |
| |
|
Hebridae |
| |
|
Hydrometridae |
| |
|
Mesoveliidae |
| |
|
Nepidae |
| |
|
Notonectidae |
| |
|
Ochteridae |
| |
|
Pleidae |
| |
|
Veliidae |
| |
Lepidoptera |
Pyralidae |
| |
Megaloptera |
Sialidae |
| |
Trichoptera |
Calamoceratidae |
| |
|
Ecnomidae |
| |
|
Hydrobiosidae |
| |
|
Hydropsychidae |
| |
|
Hydroptilidae |
| |
|
Leptoceridae |
| |
s.o. Zygoptera |
Coenagrionidae |
| |
|
Isostictidae |
| |
|
Protoneuridae |
| Malacostraca |
Amphipoda |
Talitridae |
| |
Decapoda |
Atyidae |
| |
|
Palaemonidae |
| |
|
Parastacidae |
| |
Isopoda |
Cirolanidae |
| |
|
Oniscidae |
| s.c. Oligochaeta |
– |
Oligochaeta |
| Ostracoda |
– |
Ostracoda |
|