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Pristine : Providing Basic Biophysical Information for Future Management Emma Murray1, Lynda Radke, John Creasey, Ashwin Dyall, Andrew Heap, Brendan Brooke, David Beard and David Ryan

1 Geoscience , GPO Box 378, , ACT, 2601, www.ga.gov.au [email protected]

Abstract The Near-Pristine Estuaries project in the Coastal CRC aims to improve our understanding of near-pristine coastal waterways from a national perspective by collating and synthesising existing data, and mapping the habitats of these systems. During the NLWRA, the habitats of 537 coastal waterways around Australia were mapped. However, only 41 of those chosen for mapping were in near-pristine condition. This project will redress this gap by providing mapped habitat areas for ~130 near-pristine estuaries. The data obtained will be used to improve existing conceptual models, especially of tidal creeks, and to help elucidate the human imprint on Australia’s coastal ecosystems.

Key Words: Sedimentary habitats, OzEstuaries website, Tropical estuaries

Introduction During the National Land and Water Resources Audit (NLWRA; 1), roughly half of Australia’s estuaries were classified as “near-pristine”. “Near-pristine” estuaries are those with relatively little or no apparent human impact. Little is known about these systems as they largely exist along the remotest and least explored parts of Australia’s coastline, such as far northern Australia and southwest Tasmania (Figure 1). Much of what we know about estuaries comes from studies in more accessible areas of Australia, such as the southeast and southwest coasts, where estuaries are often quite altered by human activity.

Figure 1. The locations of near-pristine coastal waterways in Australia.

There is a perceived need to learn more about pristine estuaries from both scientific and protective management perspectives. Near-pristine coastal waterways contain important baseline information for comparisons between regions and systems, in terms of water quality, ecology, and geomorphology.

The Near-Pristine Estuaries Project in the Coastal CRC aims to improve our understanding of Australia’s near-pristine coastal waterways by collating and synthesising existing data and information, and by mapping habitat areas of a representative number of these systems. During the NLWRA, the habitats of 537 coastal waterways were mapped; however, only 41 of those chosen for mapping were in near-pristine condition. This project will redress this gap by providing mapped habitat areas for ~130 of the 424 currently unmapped near-pristine estuaries. The data obtained will be used to improve existing conceptual models (2), especially of tidal creeks, and to help elucidate the human imprint on Australia’s coastal ecosystems.

What Exactly is a “Pristine ”? Defining what is meant by “pristine” can be problematic. Whether an estuary is classified as pristine or not really depends on the criteria used, which in turn is dependent on the available data. We use the classification of the NLWRA (Table 1), which was based on quantitative and qualitative information, and expert opinion on the part of State and the Territory governments (1).

Table 1. The criteria for near-pristine estuaries used by the NLWRA (1).

Physical Condition Characteristics Catchment natural cover >90% Land use Limited roads and disturbance to natural conditions and processes Catchment hydrology No dams or impoundments, virtually nil abstraction Tidal regime No impediments to tidal flow, changes from natural morphology (e.g. Training walls, barrages, bridges and causeways) Wetlands intact in vegetation and hydrology, no alterations to flood pattern Estuary use Extractive activities limited to indigenous or limited and sustainable commercial and recreational fishing, no aquaculture Pests and weeds Minimal impact on estuary from catchment weeds and limited pests and weeds within estuary Estuarine ecology Ecological systems and processes intact (e.g. benthic flora and fauna)

Habitat Mapping As a measure of the spatial extent of different types of estuarine habitats, geomorphologically distinct areas of the estuaries (geomorphic habitats) will be mapped using aerial photographs and satellite images. The project will map approximately ~130 near-pristine estuaries, selected to achieve a representative sample in terms of: geomorphic classification (2) and coastal geomorphic regions (3). Where possible, ~30 estuaries will be mapped from each of the seven geomorphic classes (Table 2) and spread across the six geomorphic regions (Figure 2). These geomorphic regions divide the Australian coastline on the basis of tide, wave, and characteristics. For example, the North-East Coast is characterised by high tidal energy, low wave energy, and high summer and low winter river energy, whereas the South-East Coast is characterised by high wave, low tide, and moderate year round river energy. State and Territory preferences will also be taken into account.

The final maps will comprise industry-standard ARC GIS files consisting of a base map of the estuary boundary, and vector layers showing a range of sub-aerial, tidal, and sub-tidal environments. The maps will add to those already mapped by the NLWRA, which are currently available for viewing and download in the Online GIS in OzEstuaries (www.ozestuaries.org; follow the OnLine GIS link).

Table 2. The seven geomorphic classes of coastal waterway (2).

Classification Landward (Nearer to Middle (Centre or Seaward (Entrance or Comments the river or main water body) mouth adjacent to the catchment) open ocean)

Embayment, (EMB) Highly variable river- Deep broad basin Wide, unconstricted Marine conditions prevail (Wave- or Tide- derived sediment and flanked by narrow entrance, large water throughout system. May Dominated) freshwater input, intertidal zone, and exchange with the sea. evolve into an estuary unrestricted wave exposed bedrock and with time. penetration. rocky reef.

Wave-dominated River-derived Broad, low energy Entrance constricted by a Sediment is mostly Estuary, (WDE) sediment and central basin, flanked barrier, that attenuates trapped in the central freshwater input by small areas of tides within the estuary. basin. Limited oceanic dominates. Fluvial- intertidal Marine sediment water exchange bayhead delta environments. dominates development

Wave-dominated Riverine sediment Channel(s) act as a Constricted entrance Represents a WDE Delta, (WDD) input. Floodplain/ conduit for transport of characterised by a barrier mostly infilled by alluvial plain, shifting sediment offshore, and tidal delta deposits, sediment. River inputs are channel. flanked by thin export of sediment to the predominantly transported intertidal areas. sea. offshore.

Coastal Lagoon/ Very little (or no) Low energy central Intermittent entrance (often Similar to a small WDE. Strandplain, freshwater and river- basin dominates. closed) characterised by Frequently isolated from (CL/SP) sediment input. No Flanked by small areas barrier and tidal delta the sea, and slow infilling. fluvial-bayhead delta of intertidal deposits. Tides environments. attenuated/excluded.

Tide-dominated Riverine sediment Wide tidal channel Wide funnel-shaped Shifting channels and Estuary, (TDE) input. Floodplain/ network, flanked by entrance containing tidal sand banks, fine alluvial plain. large areas of inter- & sand banks, large tidal sediments trapped in sub-tidal exchange. inter- & sub-tidal environments. environments.

Tide-dominated Riverine sediment Tidal channel network Wide funnel-shaped Represents a TDE mostly Delta, (TDD) input. Floodplain/ acts as conduit for entrance containing tidal infilled by sediment. River alluvial plain, shifting sediments. Smaller sand banks that may have inputs are predominantly channel. intertidal area. merged with intertidal transported offshore. environments.

Tidal Creek, (TC) Very little (or no) Wide channel network Wide funnel-shaped Similar to a TDE, contains freshwater and river- flanked by large areas entrance that does not sediment derived from sediment input. No of inter- & sub-tidal contain tidal sand banks, marine sources only fluvial-bayhead delta environments. large tidal exchange.

Figure 2. The six main coastal geomorphic regions in Australia (3).

Baseline Geomorphology Information from near-pristine coastal waterways will be used to quantify the natural variability of geomorphic and sedimentary environments (geomorphic habitats) that comes about without the significant overprinting effects of human activities. These baseline data will be compared with data for modified systems to make an assessment of the relative effects of humans on the diversity and abundance of geomorphic habitats in Australia’s coastal waterways. This is just one example of how basic biophysical information can help with the protective management of Australia’s coastal waterways for better conservation values.

Collation and Synthesis of Existing Knowledge A comprehensive literature review will collate and synthesise existing biological, chemical, and physical information on near-pristine estuaries. It will also summarise current management of near-pristine estuaries and identify information gaps, needs, and suggestions for management. In addition, it has become apparent, through talks with researchers and managers, that some near-pristine estuaries may need reclassification as they are currently being impacted by such things as aquaculture and grazing.

Information Wanted If you have worked on or know of existing studies on any near-pristine coastal waterways, the project team would like to know about your experience or findings (see list below). Your thoughts on the concept or definition of pristine estuaries would also be appreciated.

References: (1) NLWRA 2002. Australian Catchment, River and Estuary Assessment 2002. Commonwealth Government, Canberra. www.audit.ea.gov.au/ANRA/atlas_home.cfm (2) Ryan, D. A., Heap, A. D., Radke, L., and Heggie, D. T., 2003. Conceptual models of Australia’s estuaries and coastal waterways: applications for coastal resource management. Geoscience Australia, Record 2003/09, 127 pp. An online version of the information contained in this report is at: www.ozestuaries.org under the “Conceptual Models” link. (3) Harris, P.T., Heap, A.D., Bryce, S.M. Porter-Smith, R., Ryan, D.A., and Heggie, D.T. (2002). Classification of Australian Coastal depositional environments based upon a quantitative analysis of wave, tidal and fluvial power. Journal of Sedimentary Research 72 (6), 858-870.

Major implication for Future Coastal Management (1) Providing baseline data for measuring change from ‘natural’ conditions and future change in pristine estuaries. 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