Recovery of the red-finned blue-eye: an endangered fish from springs of the Great Artesian Basin (original) (raw)

Fishes in a changing world: learning from the past to promote sustainability of fish populations

Journal of Fish Biology, 2018

Populations of fishes provide valuable services for billions of people, but face diverse and interacting threats that jeopardize their sustainability. Human population growth and intensifying resource use for food, water, energy and goods are compromising fish populations through a variety of mechanisms, including overfishing, habitat degradation and declines in water quality. The important challenges raised by these issues have been recognized and have led to considerable advances over past decades in managing and mitigating threats to fishes worldwide. In this review, we identify the major threats faced by fish populations alongside recent advances that are helping to address these issues. There are very significant efforts worldwide directed towards ensuring a sustainable future for the world's fishes and fisheries and those who rely on them. Although considerable challenges remain, by drawing attention to successful mitigation of threats to fish and fisheries we hope to prov...

Finding forgotten fishes, the search for two endangered species in the NSW Murray Catchment

Executive summary Background Populations of Southern pygmy perch (SPP; Nannoperca australis) and Flat-headed galaxias (FG; Galaxias rostratus) were historically found throughout the Murray–Darling Basin (MDB), but have undergone significant reductions in both range and abundance, particularly in the NSW Murray River region. Management interventions are urgently required to protect, maintain and assist their recovery; however, such interventions require a detailed understanding of the abundance and distribution of the two species within preferred habitats. This project was undertaken to improve the understanding of the abundance and distribution of SPP and FG within the Murray LLS region, to aid in informing conservation of the remnant population and the re-establishment of additional viable populations of each species. The objectives of the project were to determine: 1. the current distribution and relative abundance of SPP in the Coppabella-Jingellic Creek system within the context of the creek’s habitat conditions, as well as to contribute to a longer term monitoring program assessing SPP population trends in the creek over time (Chapter 2: Fish assemblage and habitat sampling in Coppabella Creek). 2. if populations of SPP are present in additional creeks with similar characteristics to Coppabella Creek within the Upper Murray region (Chapter 3: Targeted SPP surveys in creeks throughout the Upper Murray region). 3. if populations of SPP and FG are still persisting in wetlands within the Murray region, and if there are any additional populations that have not previously been detected throughout the region (Chapter 4: Targeted SPP and FG surveys in wetlands throughout the Murray region). Findings  The SPP population in the Coppabella-Jingellic Creek system is still present and is recovering from the population decline experienced during the 2010–12 floods, although the population declined again in 2017 (Chapter 2).  From 2011–17, the population was limited to the upper four sites in the creek.  Habitat mapping determined that this is the remaining location of complex macrophyte communities.  Further, Carp and Redfin perch are excluded from these upstream sites owing to the Clearsprings Weir barrier (Chapter 2).  No SPP were captured from any of the Upper Murray creek sites (Chapter 3) or Murray wetland sites (Chapter 4).  Likewise, we did not manage to capture any FG from the Murray wetland sites (and Tintaldra) either (Chapter 4). The team did, however, capture an individual Galaxias oliros (Obscure galaxias).  Native fish diversity and abundance in the majority of wetlands sampled was very low. Management implications and recommendations:  To facilitate the recovery and conservation of the SPP population in the Coppabella-Jingellic system, the system should be managed with an ongoing view towards conserving the current core habitat (i.e. the deepest and most permanent pools) and complex macrophytes in the upstream reaches of the creek.  Efforts should be put into maintaining the exclusion of Carp and other alien species (e.g. the predatory Redfin perch and Brown trout) at the current Clearsprings Weir barrier in the Coppabella-Jingellic system. Threatened Species Surveys Charles Sturt University and NSW Department of Primary Industries 4  Trout or other species that may prey on SPP should not be stocked in the Coppabella-Jingellic system.  Given the importance of macrophyte communities in forming suitable habitat for SPP, habitat works that facilitate the regeneration and conservation of complex macrophyte species' should form a central component of any management plan for the Coppabella-Jingellic system.  Murray LLS and NSW DPI are currently considering the construction of a new alien fish exclusion barrier below Clearsprings Weir. If this new barrier was able to successfully exclude Carp from the upstream section of the Coppabella-Jingellic Creek system, then it would theoretically allow more complex macrophyte communities to return to these reaches, and thus provide more suitable habitat for the re-expansion of the SPP population lower down the system.  Physical removal of any existing alien species in the section above the proposed new barrier will be required.  The proposed new barrier would also provide a secondary buffer against alien species incursion for the current Coppabella-Jingellic Creek SPP population as well.  Nevertheless, the installation of any barrier comes with a range of risks for the passage of native fish (in addition to alien fish) by blocking longitudinal movements. So these risks would need to be thoroughly assessed and mitigated before the construction of any such barrier proceeds past the scoping phase. All of the native species present in the Coppabella-Jingellic Creek system are non-migratory, and considered relatively sedentary, so impacts should be relatively benign, relative to the benefits.  Other general habitat management actions for both SPP and FG (whether they be at sites associated with the Coppabella-Jingellic system, the Upper Murray creeks, or the Murray wetlands) should include (1) the sustained control of blackberries, willows and other pest plant species, since these shade and compete with the native riparian and aquatic plant communities; (2) stock exclusion from the riparian zone, especially during dry periods when effects upon the macrophyte communities are likely to be exacerbated; and (3) restoring native terrestrial vegetation, but at a sufficient distance from the stream so as not to shade and/or hinder the favourable growth of macrophyte communities in any way.  Consideration should also be given to identifying suitable alternative sites for potentially establishing additional SPP and FG populations. These sites would obviously need to meet a number of criteria in order to offer any chance of success. Specifically, at a minimum, they would need to: (1) provide a secure water source that persists during droughts; (2) have an abundance of appropriate complex macrophytes for suitable habitat; and (3) they would need to have no or very low numbers of alien fish species and be secure from future invasions (e.g. have a barrier or screen to prevent such events).  The present study considered three upper Murray creek sites as potential reintroduction sites for SPP: Basin Creek, Doughtys Creek and Maragle Creek. Our findings suggested that Basin Creek may offer the most suitable habitat conditions out of these three sites for reintroducing SPP, since it had a relatively high proportion of pool habitat and macrophyte cover, and no alien fish were detected there.