Reef 
Research: Volume 6 No. 3 September 1996
What's out there?

Shoalwater Bay update:
DISCOVERING THE FORGOTTEN WETLANDS

Ray Berkelmans

click here for figure 1.
(size: 53 kb)
The Inquiry into Shoalwater Bay, which considered the relative merits of military, conservation, fishing and mining use of the area, concluded that Shoalwater Bay has wetlands of exceptional value and that it is an important scientific reference area. Resource surveys commissioned by the Great Barrier Reef Marine Park Authority after the Inquiry in support of management planning for this area are putting substance to these conclusions and show that they are not overstated. Here are some preliminary results of projects currently under way.

SEAGRASS STUDIES
Warren Lee Long, Len McKenzie and Rob Coles
D
etailed surveys of seagrass meadows were conducted using helicopter reconnaissance, aerial photos, satellite imagery and dive surveys. A total of 126 ± 8 km2 of seagrass habitat was mapped in the spring survey which was conducted in October 1995. This figure is nearly double the estimate of seagrass coverage found in the broad-scale surveys conducted in 1987 and represents around 5% of the total inshore seagrass habitat in the Great Barrier Reef Region. It is by far the largest seagrass area south of Cooktown and compares with 50 km2 in the Hinchinbrook area, 47 km2 in Cleveland Bay and 61 km2 in the Whitsunday area, based on the 1987 broad-scale survey data (GBRMPA Geographical Information System). The dominant seagrass communities consisted mainly of Zostera capricorni (54% cover) and Halodule/Halophila (44%). A significant finding of this survey was that the most of the seagrass meadows (75%) were restricted to the intertidal banks and drainage channels, up to 0.7 m above mean sea level (figure 1). This has special implications for the management of the large turtle and dugong populations which rely on these meadows for their food. Turtles and dugongs are restricted in their feeding times to high tides, a feature supported by the stranding of literally hundreds of turtles on the low tide. The restricted distribution of seagrass beds makes dugongs and turtles especially vulnerable to conflicting human activities on the intertidal mud banks, such as gill netting. Under provisions of the Queensland Fisheries Regulations, gill netting on the foreshore in Shoalwater Bay was banned in late 1995.

The Shoalwater Bay seagrass beds are likely to be significant to regional fisheries production. Commercially important prawns were found at each of the seagrass beds which were sampled and represented 99% of the prawns sampled. The western king prawn was the most abundant of the commercial species, but the true endeavour prawn, red endeavour prawn and brown tiger prawn were also common in the seagrass beds. The abundance of other invertebrates and juvenile fish found in beam trawl samples also indicate a significant source of food in local marine food webs.

Monitoring sites were established on selected meadows which are intended for survey every two years. A complete post-wet season mapping survey was undertaken in April 1996, the results of which are currently being analysed.

FRINGING REEF SURVEYS
Tony Ayling
photo: Mumford Island
Mumford Island in the north-east of Shoalwater Bay is typical of most of the islands in the area being made up of a series of granite/basalt islets with small beaches with a surrounding fringing reef.
A
lthough Shoalwater Bay is mostly known for its wetlands, it contains over 50 islands (most are tiny islets), many of which have fringing corals reefs. None of these reefs had been surveyed prior to the Inquiry.

Eighteen reefs were surveyed and ranked according to their ecological value (Done 1995). Coral cover was very variable ranging from sparse (7%) on fringing reefs dominated by the macroalga, Sargassum, to high (66%). Most fringing reef community types were dominated by acroporids and Montipora species, but extensive stands of Turbinaria frondens were also common. For most species of coral, sizes were smaller than those found in most fringing reefs, but for plate-forming Acropora, many unusually large colonies were found (up to 5 m in diameter!). Many colonies of Turbinaria frondens were also found in the size class 2-5 m, the largest single colony measuring 4.55 m x 3.85 m! The best reefs (in terms of bioconstuction and biodiversity) were generally found in the north-east of Shoalwater Bay.

The diversity of corals was moderately low with a total of 87 species found in Shoalwater Bay (over a total of 25 diving hours), compared with 120 species found in inshore fringing reefs in the Cairns area (30 diving hours), 131 species at Dent Island in the Whitsunday area (2 diving hours) and 143 species around Cape Tribulation fringing reefs (10 diving hours). However, a number of species were found which are considered 'rare' on the Great Barrier Reef (Veron 1986), although some may be common in temperate waters. These include Acanthastrea hillae, Acanthastrea bowerbanki, Favia maritima, Acropora glauca, Acropora solitariensis and Turbinaria bifronds. These species were found at nearly all sites. Another interesting feature of coral diversity was the notable absence of many species, and indeed whole genera, which are found on most fringing reefs to the north. These include Echinopora (all species), Pectinia (all species), Oxypora (all species), Pavona (all species), Fungidae (all genera, except Podabacea crustacea), Millepora tenella, Merulina ampliata, Porites cylindrica, Acropora humilis and Acropora gemmifera.

FISHERIES REVIEW
Fisheries Group, Queensland Department of Primary Industries
T
he Shoalwater Bay area supports only small scale commercial, charter and recreational fisheries compared to the rest of the Queensland east coast, but the fisheries are important to the local economy. The area covered by Shoalwater Bay, however, is disproportionately large in relation to the total commercial fish catch. The low catch is probably a result of a number of factors, including the remoteness of the area, the large number of Defence Closures, the zoning restriction to trawling in most of Shoalwater Bay proper (General Use 'B') and navigational difficulties due to the large tidal range in the area (up to six-metre tides).

In terms of the proportion of Queensland's total commercial fish catch, the Shoalwater Bay area contributes around 1% of the state's finfish, of which blue salmon is the dominant species. An average of 16 tonnes of blue salmon are caught annually, representing around 12% of Queensland catch. Other major species in the finfishery are shark, barramundi, mullet and grey mackerel, each representing between 0.3-3% of the state's catch (see figure 2 below). With the exception of shark and mackerel, almost all finfish are caught by gill netting. This has resulted in an unknown, but probably large, number of dugong deaths in the area. The restriction on gill netting on the foreshore in Shoalwater Bay, which was proclaimed in late 1995, may reduce future effort and catch in this fishery.

FIGURE 2. diagram

Figure 2. Average annual finfish catch and its relative importance to total Queensland production

The trawl fishery effort is concentrated immediately east of Shoalwater Bay between Townshend Island and Corio Bay with total prawn catches averaging 85 tonnes per annum, representing around 1% of the state's total prawn catch. Banana and endeavour prawns are the dominant species caught. Banana prawn are the major species caught and represent around 46% of the total prawn catch in the Shoalwater Bay area. However, catches have been highly variable from year to year, ranging from 7 to 85 tonnes between 1988 and 1994, and show a strong positive correlation with rainfall. By-catch from trawling is undocumented for this area, except for incidental capture of turtles. A voluntary logbook program (Queensland East Coast Otter Trawl Fishery) shows that 14 turtles were caught between 1991 and 1994 in the Shoalwater Bay area, but none died.

Other fisheries of note are the mud crab fishery which averaged around 29 tonnes per year between 1988 and 1994, which represents around 8% of the Queensland catch, and the oyster fishery which averaged around 7% of the state's catch.

The status of exploited fish stocks are unknown. Catch statistics from the Queensland commercial fishing database, C- FISH, show highly variable catches for most fisheries over the six years between 1988 and 1994 and allow no conclusions to be drawn.

Most of the commercial species caught are mangrove/ estuarine specialists and, given the vast area of mud banks, seagrass beds, couch flats and mangrove forests in Shoalwater Bay, it is likely that the intertidal habitats contribute appreciably to fisheries resources. However, the extent, value and nature of the interaction between nursery/habitat areas and fisheries production is unknown.


References

Done, T.J. 1995, 'Ecological criteria for evaluating coral reefs and their implications for managers and researchers', Coral Reefs, 14:183-192.

Veron, J.E.N. 1986, Corals of Australia and the Indo- Pacific, University of Hawaii Press, Honolulu, 644 pp.


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Great Barrier Reef Marine Park Authority
PO Box 1379 TOWNSVILLE QLD 4810. Phone: (077) 500 700, Fax: (077) 726 093
E-mail: registry@gbrmpa.gov.au