Image

Walpole River - Plain Road Downstream

Basin : Shannon river

Catchment : Deep River

River condition at the Plain Road Downstream site (site code: DR15WALP1, site reference: 6064006) on the Walpole River has been assessed as part of the Healthy Rivers Program (Healthy Rivers), using standard methods from the South West Index of River Condition (SWIRC). The SWIRC incorporates field and desktop data from the site and from the broader catchment. Field data collected include the following indicators, assessed over around a 100 m length of stream:

    • Aquatic biota: fish and crayfish community information (abundance of native and exotic species across size classes, general reproductive and physical condition)
    • Water quality: dissolved oxygen, temperature, specific conductivity, and pH (logged in-situ over 24 hours), as well as laboratory samples for colour, alkalinity, turbidity and nutrients
    • Aquatic habitat: e.g. water depth, substrate type, presence of woody debris and detritus, type and cover of macrophytes and draping vegetation
    • Physical form: channel morphology, bank slope and shape, bioconnectivity (barriers to migration of aquatic species), erosion and sedimentation
    • Fringing zone: width and length of vegetation cover within the river corridor and lands immediately adjacent, structural intactness of riparian and streamside vegetation
    • Hydrology: measures of flow (velocity) at representative locations (compared against data from stream gauging stations within the system)
    • Local land use: descriptions of local land use types and activities (compared against land use mapping information for the catchment)

This is the first assessment of this site using the SWIRC methods. At this time no previous assessments of river ecology had been reported.

Assessments are listed below:

  • 2020 – summer (16–17 March): Healthy Rivers

Other data: The Plain Road Downstream site is about 1.1 km downstream of the Walpole Weir and gauging station. The gauging station is owned by Water Corporation and is known as the Plain Road Bridge gauging station (this gauging station is currently not monitored; site reference: 606003).

Search on the site code or site reference in the Department of Water and Environmental Regulation’s Water Information Reporting (WIR) system to find data for this site and nearby sampling points (flows, surface water quality, groundwater monitoring, department’s meteorological data). See also the Bureau of Meteorology website for additional meteorological data for the area.

Condition summary

A complete condition summary for this site has not yet been published. Please contact the department’s River Science team for site data (please provide the site code and sampling dates).

The image below indicates conditions at the time of sampling in March, towards the end of the dry season. March is within the Noongar season of Bunuru, which is generally the driest and hottest part of the year. Further images are provided in the gallery at the bottom of the page, to show general site conditions.

Walpole River

Walpole River, March 2020

An overview of aquatic species found at the site is provided in the next section.

Species found at the site

Fish and crayfish

The aquatic biota community in this subcatchment is one of the highest recorded across the South West of Western Australia. Thirteen native species were recorded in this subcatchment in the March 2020 assessment. The species recorded at the assessment site includes three native freshwater fish (little pygmy perch, western pygmy perch and common jollytail), five native estuarine-freshwater fish (south-western goby, blue-spot goby, western hardyhead, sea mullet and southern black bream) and one native crustacean (south-west glass shrimp). Four additional species were found directly below and about 200 m downstream of the Walpole Weir during site investigations (refer to green dots on map below). These species include three native fish (nightfish, Balston’s pygmy perch and western mud minnow) and one native crayfish (smooth marron).

Notably no non-native species were recorded during this assessment.

The Plain Road Downstream site is influenced by tidal movements from the Walpole-Nornalup Inlet system. At the time of sampling, the salinity was within the hyper-salinity category with estuarine-freshwater species dominating the catch. The freshwater fish species observed at this assessment site were found in low abundance.

Four of the freshwater fish species found in this subcatchment have high conservation value, these include:

All of the above fish species except the salamanderfish were observed during the March 2020 assessments.

This is the first time little pygmy perch have been recorded in this system. It was only discovered in 2008 (formally described in 2013) and is only found in restricted areas in the southern-most part of Western Australia including Denmark, Mitchell, Hay, Kent and Walpole Rivers and Lake Smith. Little pygmy perch were found in low abundance at the Plain Road Downstream assessment site, with higher abundances recorded at the Plain Road Upstream site, upstream of the Walpole Weir.

During site investigations, Balston’s pygmy perch was found within the subcatchment about 200 m downstream of the Walpole Weir. Balston’s pygmy perch are restricted to near-coastal streams, lakes and wetlands between the upper Margaret River and the Goodga River.

The pouched lamprey (both ammocetes and adults)  were found in the Morgan and Beatty (2003) study but not detected in this assessment. The pouched lamprey is a Priority 3 species (poorly-known) under the Biodiversity Conservation Act 2016 (Western Australia). Priority 3 refers to possibly threatened species where data is insufficient to assess threatening processes that could affect them, also noting that this species is not expected to be under imminent threat based on available data.  In the early stage of their life cycle, lamprey burrow in sand in upper reaches of river systems. They migrate to the ocean where they may remain and feed for a number of years. Eventually lamprey will migrate back up river systems to spawn and die. Outside of the short migration periods, lamprey are unlikely to enter traps. The absence of lamprey from most SWIRC assessments is not a significant concern as this species typically migrates in a brief period around peak winter flow (which is largely outside of the usual assessment periods) and only in high flow years.

Salamanderfish were also found by Beatty and Morgan in 2003, however they were only recorded below the Walpole Weir but may occur elsewhere in the system. The salamanderfish was not expected at this specific sites assessed in 2020 as this species is only found in near-coastal wetland and do not typically occur within riverine habitats.

Note: collection of fauna from inland aquatic ecosystems across Western Australia requires a license from the Department of Primary Industries and Regional Development (DPIRD) and also the Department of Biodiversity, Conservation and Attractions (DBCA). All species collected must be reported to these agencies as part of license conditions.

 

Other aquatic fauna

One south-western snake-necked turtle was recorded at this assessment site.

For more info on this and other aquatic species, please see the River Science fauna page here.

References and further reading:
Beatty S and Morgan D 2003, ‘Freshwater Fishes of the Walpole River and the impact of the weir to fish and lamprey migrations’ Fisheries Western Australia

{"autoplay":"true","autoplay_speed":"3000","speed":"300","arrows":"true","dots":"false","rtl":"false"}