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Sand Whiting is a sustainable species along the east coast of Australia. It is most abundant in southern QLD and northern NSW.

Sand Whiting occurs along the east coast of Australia and is most abundant in southern Queensland and northern New South Wales. Recent tagging studies have shown movement of adult fish between estuaries separated by distances of up to 450 km and across state management jurisdictions [Gray 2023], but conclusive information on biological stock boundaries remains incomplete. The unknown nature of biological stock composition means no formal assessment at the biological stock level has been completed. Separate assessments of Sand Whiting have been conducted in Queensland and New South Wales [Hoyle et al. 2000; O'Neill 2000; Ochwada-Doyle et al. 2014; Leigh et al. 2019; Hall 2020].

Here, assessment of stock status is presented at the jurisdictional level—Queensland and New South Wales.

Queensland

The Queensland Sand Whiting jurisdictional stock is a predominantly caught in shallow coastal and estuarine waters south of Baffle Creek. The annual harvest of Sand Whiting in Queensland is shared evenly between the recreational and commercial sectors. The commercial harvest is caught using nets (mainly gillnets and tunnel nets) in the East Coast Inshore Fishery (ECIF), whereas the recreational harvest is predominantly caught by hook and line. The most recent stock assessment of Sand Whiting in Queensland (based on 2017 data) estimated the exploitable biomass to be at 29% of unfished biomass [Leigh et al. 2019]. This corresponds to an approximate maximum sustainable yield (MSY) but is below the target biomass of 60% unfished biomass set in Queensland’s Sustainable Fishing Strategy (2017–2027) [QDAF 2017]. Since 2007, both size and age frequencies of commercial and recreational harvests have been largely consistent between years, indicating a stable population with continued recruitment [QDAF 2023, unpublished data]. The above evidence indicates that the biomass of this stock is unlikely to be depleted and that recruitment is unlikely to be impaired. 

Fishing pressure has remained relatively stable between 1945 and 2009 for commercial harvest, albeit with some variability between years. Since 2009–10 however, the harvest has been in intermittent decline. In 2021–22, the commercial harvest reached a historic low of 74 t; representing a decline of more than two-thirds compared to the long-term historical averages based on commercial logbook data (1988–2021: 263 t) and Queensland Fish Board data (1945–80: 266 t) [Leigh et al. 2019]. Over the same period the sector experienced a 75 per cent decline in nominal effort (2009–10: 5,163 boat days; 2021–22: 1,287 boat days). The onset of this decline in effort coincided with spatial closures within key commercial fishing grounds. In 2009, 23% of the Moreton Bay Marine Park was closed to commercial net fishing (van de Geer et al. 2013). A series of subsequent license buybacks along with structural adjustment packages saw the number of net license holders targeting Sand Whiting in the region reduce by half (a decline of 75 licenses between 2009–10 and 2021–22). 

Sand whiting consistently rank as one of the most popular species targeted by the recreational sector in Queensland, in terms of numbers harvested [QDAF 2021a]. The species is predominantly caught by hook and line in combined catches with congeneric species including Goldenline Whiting (S. analis) and Northern Whiting (S. sihama). The most recent statewide recreational fishing survey estimated that approximately 65.6 t of Sand Whiting complex (i.e. comprising catches of “Sand Whiting” or “Whiting - unspecified”) was harvested in 2019–20 [Teixeira et al. 2021]. This was lower than the harvest estimates from previous survey years (102.3 t, 124.8 t and 453.5 t in 2013–14, 2010–11 and 2000–01 respectively) [Henry and Lyle 2003; Taylor 2012; Webley et al. 2015]. There are no direct estimates of recreational fishing effort targeting Sand Whiting in Queensland. However, there is some evidence for a decline in effort targeting whiting (Sillago spp.) since 2000. According to diary surveys, approximately 126,000 days were spent targeting whiting in Queensland waters in 2013–14; compared to 194,000 days in 2010–11 and 361,000 days in 2000–01 [Webley et al. 2015].

Fishing pressure for Sand Whiting is managed under ECIF Harvest Strategy (2017–2026) [QDAF 2021b]. A total allowable commercial catch (TACC) limit of 162 t per year was introduced on 1 September 2021. By the end of the 2022 season, approximately 46% of the commercial quota remained unused. In 2009, a combined in-possession limit of 30 whiting (Sand, Goldenline and Northern Whiting) was applied to the recreational sector with the aim of reducing fishing mortality. The current minimum legal size for Sand Whiting in Queensland (230 mm TL) allows a proportion of mature fish to spawn at least once [Ochwada-Doyle et al. 2014]. The current level of fishing mortality is unlikely to cause the stock to become recruitment impaired. 

On the basis of the evidence provided above, Sand Whiting in Queensland is classified as a sustainable stock.

Sand Whiting biology [Burchmore et al. 1988; Gray 2023; McKay 1992; Ochwada-Doyle et al. 2014; Stocks et al. 2011]

Queensland – Indigenous (Management Methods). For more information see: https://www.daf.qld.gov.au/business-priorities/fisheries/traditional-fishing

Queensland - Commercial (Catch). Queensland commercial and charter data has been sourced from the commercial fisheries logbook program. Further information available through the Queensland Fisheries Summary Report: https://www.daf.qld.gov.au/business-priorities/fisheries/monitoring-research/data/queensland-fisheries-summary-report

Queensland - Recreational Fishing (Catch). Data based at the whole Queensland level and derived from statewide recreational fishing surveys. Where possible, estimates have been converted to weight (tonnes) using best known conversion multipliers. Conversion factors may display regional or temporal variability. In the absence of an adequate conversion factor, data presented as number of fish.

Queensland – Commercial (Management Methods). Harvest strategies are available at: https://www.daf.qld.gov.au/business-priorities/fisheries/sustainable/harvest-strategy

New South Wales – Commercial (Catch). Data are provided for financial years.

New South Wales – Recreational (Catch). Estimates from Murphy et al. [2020, 2022], based on a survey of Recreational Fishing Licence households.

New South Wales – Indigenous (Management Methods). https://www.dpi.nsw.gov.au/fishing/aboriginal-fishing

Commercial catch of Sand Whiting - note confidential catch not shown

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2. Gray, CA, 2023, Connectivity and variation among estuaries in recruitment and population demographics of Sillago ciliata. Ichthyological Research, 70(1): 50-66.
3. Hall, KC 2020, NSW Stock status summary 2018/19 – Sand Whiting (Sillago ciliata). NSW Department of Primary Industries, Coffs Harbour, NSW.
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16. Queensland Fisheries, Department of Agriculture and Fisheries 2017, Queensland Sustainable Fisheries Strategy 2017-2027, Brisbane, Queensland. Available at: https://www.publications.qld.gov.au/dataset/155ccffb-3a30-48c1-8144-7892e8a57339/resource/319c7e02-f07b-4b2e-8fd5-a435d2c2f3c9/download/qld-sustainable-fisheries-strategy.pdf (Accessed: 29 September 2023).
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18. Stocks, J, Stewart, J and Gray, CA 2011, Using otolith increment widths to infer spatial, temporal and gender variation in the growth of sand whiting Sillago ciliata, Fisheries Management and Ecology, 18: 121–131.
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