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    This is one antioxidant gummy that you can have when you need it the most. Divergence inferences from the fossil record can only be based on available fossils and cannot account for undiscovered material or species that no left fossilised remains. Consequently, divergence times estimated from the fossil record are usually underestimated Anderson, The most recent common ancestor of carp and catfish therefore lived tens, and perhaps hundreds, of millions of years ago.

    Thus, catfish are indeed the Australian native fishes most closely related to carp, but this not imply that the evolutionary relationship is particularly close.

    The degree of taxonomic relatedness between carp and catfish may be contextualised by a general overview of the taxonomic hierarchy the scheme scientists use to classify living things. Kingdom is the broadest level of biological classification. For example, all multicellular animals, whether mosquitos or elephants, are classified into the Kingdom Animalia. Taxonomists in Australia, Great Britain, and several other countries generally recognise five kingdoms; Animalia, Plantae, Fungi, Protista, and Monera, while American taxonomists sometimes divide the Kingdom Monera bacteria into two kingdoms Archaeabacteria and Eubacteria , making a total of six kingdoms.

    The Phylum is another very broad level of classification. For example, the Phylum Chordata includes all vertebrates and some invertebrates. The defining features of chordates animals within the Phylum Chordata are possession, at some stage in the life-history, of:. Thus, human beings and indeed all mammals , birds, reptiles, amphibians, fish, and some invertebrates, such as sea squirts, all belong in the Phylum Chordata.

    There are approximately animal classes, although this number can vary based on taxonomic revisions. As an example of the degree of relatedness implied by this taxonomic rank, human beings belong in the class Mammalia, along with all other mammals i. Focussing specifically on fish, the class Actinopterygii, to which carp and catfish both belong, includes all fishes apart from sharks, rays, and jawless fishes lampreys, hagfish. Thus, for example, carp, catfish, barramundi, all tunas, marlin, mullet, gudgeons, gobies, coral trout, Murray cod, and approximately 24, other fish species are all actinopterygians.

    Order is the taxonomic rank at which carp order Cypriniformes and catfish order Siluriformes diverge. To place the concept of order in context, human beings belong in the order Primates, along with lemurs, lorises, tarsiers, monkeys, and apes.

    Domestic dogs belong in the order Carnivora, along with cats including the big cats , seals, walruses, weasels, skunks, hyaenas, and many other predatory mammals. At this taxonomic rank, carp and catfish have now diverged. The order Cypriniformes is divided into families, with common carp Cyprinus carpio belonging to family Cyprinidae.

    The order Siluriformes, to which catfish belong, contains more than 30 families. The two catfish species tested for susceptibility to Cyprinid herpesvirus 3 belong to two separate families, Ariidae forktail catfishes and Plotosidae eel-tailed catfishes.

    Organisms sharing this taxonomic rank are closely-related. Introduced common carp are the only species from the genus Cyprinus occurring in Australia. Human beings belong to the genus Homo. Individuals within a species can interbreed to produce fertile offspring. The common carp is a species; Cyprinus carpio , while modern humans are also a species; Homo sapiens.

    A scientific name for a species thus comprises the genus name e. Cyprinus , which is shared by all species within that genus, and the specific epithet e. Taxonomists are sometimes interested in defining sub-species, a finer classification again, but this level of detail is unnecessary for the present discussion. Table 1 in this scientific paper gives the full mortality results from the susceptibility trials.

    As has been noted, levels of mortality sometimes quite high were, indeed, observed in some native species that were tested. However, as stated in the paper:. In a further 10 cases, mortalities in negative control groups matched, or exceeded, those in viral-challenged counterparts, suggesting that CyHV-3 was not affecting these NTS. Mortalities in negative-control fish were clearly not due to virus because at no stage were these fish exposed to the carp herpesvirus.

    So, mortalities in negative-control fish suggested that other factors could account for the losses, not only of negative-control fish, but also of fish in the virus-challenged groups. Stress associated with bringing wild fish into a very unfamiliar environment would likely be an important factor.

    The effects of existing parasite burdens in many wild-caught fish species would also have been exacerbated by the stress of captivity. While this is the optimal temperature for virus activity, it is not necessarily the optimal temperature for all fish species that were examined. And finally, the methods used to challenge fish with virus were undoubtedly stressful. All fish species were examined by bath exposure to the carp herpesvirus simulating the potential natural route of infection.

    This involves fish swimming in a high-protein, aqueous solution that contains high levels of virus or, for negative controls, the same solution but without virus. While the protein solution is not toxic, it probably does interfere to some extent with oxygen exchange across the gills.

    Hence, many fish species may be stressed by this process, some more than others, and this probably accounts for some subsequent mortalities in virus-challenged, and negative-control groups. In many cases, fish were also challenged by direct inoculation of the virus into the fish, or, for negative-controls, inoculation of an equivalent volume of an innocuous fluid.

    While this procedure was only conducted on relatively robust species of fish, the anaesthesia and handling involved in this process would also no doubt stress many fish. In other words, in these 4 instances, mortality in virus-challenged fish was greater than in the negative controls.

    However, when the cause of this mortality was investigated further, there was no evidence to incriminate the carp herpesvirus. Firstly , most of the mortalities occurred far too early, or too late, in the course of infection to be consistent with the carp herpesvirus Figure 1 in the journal paper. Secondly , using highly sensitive and specific molecular tests a combination of a PCR test, and an RT-PCR test with specially-designed primers , there was no evidence that the carp herpesvirus was present, or had multiplied, in any of the fish and, without virus there can be no disease attributed to the virus.

    Finally , microscopic examination of tissues from dying fish failed to reveal any changes that would be consistent with a viral infection. The remaining few, like salamanderfish from W. Clearly, it is not possible to test the susceptibility of every native fish species in Australia to the carp herpesvirus there are too many species, and not sufficient time or resources to test them all.

    So, the approach the CSIRO researchers adopted was to test the susceptibility of representative species from each of the 10 taxonomic groups of Australian freshwater, or estuarine, fish that could conceivably come into contact with an infected carp if it were to be released in Australia. The overriding aim with the susceptibility trials was to create conditions that would give the carp herpesvirus the best chance to cause disease in native fish species.

    If, in the face of such favourable conditions, the virus failed to infect or produce disease, then its safety could be assured. For this reason, small usually immature fish were purposely chosen for the challenge trials because it is these fish that have the most immature immune system.

    If any fish was going to be susceptible to the carp herpesvirus, then it would be those with immature, poorly-developed immune systems. So, again, the researchers were in some cases, inadvertently creating conditions that would give the virus the best chance to cause disease. Despite all these conditions, the carp herpesvirus was unable to multiply or cause disease in any of the native fish species that were tested.

    Larvae of native fish species were purposely not tested for susceptibility because work with the carp herpesvirus in carp the host species of the virus has shown that larvae under 1 cm are, in fact, not susceptible to infection see Ito et al, There is a low risk of the carp virus undergoing genetic changes in such a way as to result in a potentially increased risk to Australian native species. The carp virus is a DNA virus, which tend to be quite stable, increasingly so for those with larger genomes.

    The carp virus is one of the largest, and therefore most stable, viruses from its scientific family. Of course, it is important to recognise that all viruses mutate and carp herpesvirus, myxomatosis virus, calicivirus are no exception, but mutation does not directly relate to increased risk.

    Mutations very rarely equate to dangerous events such as host jumps, or increased virulence and the timeframes of such rare events are more easily quantified in terms of millions of years! That lesson comes from long term evolutionary studies and extensive observations of viruses in the wild: So, the chance of a host-jump by the carp herpesvirus in Australia would be vanishingly small simply because there are no closely-related native cyprinid species.

    At approximately , base pairs, CyHV-3 has the largest genome in the family Alloherpesviridae Fournier and Vanderplasschen, ; Davison et al. Further evidence in support of this assessment of low risk includes the lack of reports that CyHV-3 has extended its host range beyond common and koi carp in those countries where it is endemic since first recognized in the mids Aoki et al.

    Genome sequences of three koi herpesvirus isolates representing the expanding distribution of an emerging disease threatening koi and common carp worldwide. Journal of Virology , 81, Comparative genomics of carp herpesviruses. Journal of Virology, 87, — A herpesvirus associated with mass mortality of juvenile and adult koi, a strain of common carp.

    Journal of Aquatic Animal Health , 12, Journal of Fish Diseases , 18, A herpesvirus isolated from carp papilloma in Japan. Fish Shell Pathol , 32, However, science can help us to determine the probability of something occurring. And there is a low probability of the carp virus mutating or otherwise evolving in ways that would enable it to infect a new host species including Australian native species. This low risk is partly because the Carp virus is a type of virus — a double-stranded DNA virus - for which mutation of a type and magnitude that would enable infection of a new host species is not a primary mechanism of viral evolution, and partly because common carp are not closely related to any Australian native species.

    Science seeks evidence to support or refute a hypothesis or some other scientific principle like a theory. We can, however, determine whether something has a low probability of occurring. And there is a low probability that CyHV-3 will mutate once released and resulting in a potentially increased risk to non-target species. This is because the carp virus is a DNA virus, which tend to be quite stable, increasingly so for those with larger genomes. Additional evidence in support of this assessment includes the lack of reports that CyHV-3 has extended its host range beyond common and koi carp in those countries where it is endemic since first recognized in the mids Aoki et al.

    Comparative analysis estimates the relative frequencies of co-divergence and cross-species transmission within viral families. The two key components of this program will be: At the end of , the NCCP will make a formal recommendation on the best way to control carp impacts in Australia. It will be based on the results of the research projects funded by the NCCP and the input from communities during the consultation process. If it is recommended that the carp virus form part of a suite of carp-control measures, and formal approval is granted, the carp virus may then be released.

    In that case, the initial release sites and specific pattern of release would follow the results of relevant research funded under Research Theme 3: This is being investigated by the National Carp Control Plan. Scientists and planners are currently working on how to release the virus in the most effective way to reduce carp populations, but also to manage risks and impacts. Scientists are building their understanding of how the virus is likely to impact carp populations and waterways through a series of research projects funded by the NCCP, and previous research undertaken worldwide.

    This knowledge will allow more accurate predictions about how the virus is likely to work in specific waterways, and gives authorities a more precise and controlled way of reducing carp populations, while being able to manage risks. Planners are also playing a role in building more precision into how the virus could be released by mapping virus management within discrete carp control zones. These are areas of catchments and waterways bounded by significant barriers to upstream fish passage river regulating structures or natural barriers.

    These zones can then contain the impacts of the virus and allow a staged release. To control the risks of downstream, unplanned virus spread resulting from high water flows or floods the virus release can start from downstream carp control zones and then move to upstream carp control zones.

    A staged release of the virus within discrete control zones would also allow for the efficient use of management resources. Activities such as clean up could be more focussed, rather than being spread over numerous locations at the same time. Successful control of a pest species over a large geographic range can be logistically challenging, and this is certainly true of carp control in Australia.

    Identification of a strategy for staged release would help reduce logistical challenges, and this is an area of focus under the NCCP. Possible phasing of a virus release is not without challenges. In particular, effectively compartmentalising such a large, geographically, climatically, and hydrologically diverse landscape poses numerous challenges. The aim of this program was to eradicate brown rat Rattus norvegicus from a km long, 10 - 40 km wide sub-Antarctic island km east of the Falkland Islands through introduction of tonnes of poison over square miles km 2.

    This knowledge enabled development of a staged program for implementation, in which the island was divided into a number of treatment zones, which were treated individually. Using this staged, methodical strategy the project team were able to progressively move across the island, treating each zone and testing effectiveness before moving on until eventually the entire island was treated successfully.

    While there is no evidence of genetic structuring of carp in Australia, the discontinuous nature of many Australian waterways including the Murray-Darling Basin resulting from extensive installation of flow regulating infrastructure may offer a means via which the release of CyHV-3, and subsequent clean-up of carp biomass, may be logically phased.

    Under the National Carp Control Plan it is proposed to explore opportunities to utilise barriers to fish migration to separate waters into discrete treatment zones, enabling carp to be treated within each zone in a staged manner. Implementing a controlled release strategy using barriers to fish migration would require identifying in-stream structures impervious to drown-out in all but major floods, and timing release and clean-up to avoid significant flooding.

    Dead carp will occur in waterways where the virus is released. A critical challenge for the NCCP is to demonstrate how we can manage dead carp in a way which avoids impacts on water quality, people, livestock and native species.

    To meet this challenge, the NCCP is undertaking research, and talking to experts and local communities about how to respond to dead carp biomass. The response ideas that researchers, stakeholders and experts come up with will be tested and refined through regional case studies which will workshop how the virus release can be managed in a specific region.

    The case studies will involve all the relevant authorities, stakeholders who might be impacted and people with local knowledge about carp and their waterways. The NCCP has already identified a range of methods to respond to the build-up of dead carp at a wide range of locations including: The specific chosen methods for managing dead carp will depend on local conditions and arrangements. Dead carp that are removed from the waterways will be transported to regional processing facilities wherever possible.

    The NCCP has a specific research project which will recommend how the dead carp biomass can be used. Where is it not possible to use the dead carp, they will be disposed of at approved waste disposal sites. Virus response will be managed through co-ordinated regional, state and national bodies that bring together relevant government agencies and local authorities. The community and commercial sector will also be involved in the response to the virus release.

    Like any worthwhile endeavour, carp biocontrol presents some challenges. Maintaining water quality for use by people, stock, and native species is one such challenge.

    The NCCP recognises the importance of this task, and our approach to developing a practical, effective, and flexible clean-up strategies is outlined below. Fish kills in freshwater ecosystems occur world-wide, with many causes e. Research on fish kills has tended to focus on identifying causes e. Thronson and Quigg, ; Moustaka-Gouni et al. Nonetheless, published and unpublished case studies consider clean-up action to protect water quality following fish kills La and Cooke, Intuitively, we can all understand that major carp mortality events entail some risks to water quality.

    However, understanding the exact nature and magnitude of these risk may require a specialised approach. Research commissioned under the NCCP will include a scientific risk assessment quantifying risks associated with the proposed carp biocontrol program, including the clean-up.

    Successful clean-up requires understanding carp abundance and distribution at several spatial scales, from continental through to particular habitat types. The NCCP will commission a multi-method biomass study, providing the most accurate picture ever developed of carp distribution and abundance in Australia. Methods used will include:. This multi-method approach will enable cross-checking and triangulation, enhancing the accuracy and rigour of resulting biomass estimates.

    The model will identify optimal seasons, locations, and release strategies for the virus, and in so doing will also pinpoint times and places where carp mortality events are likely, allowing for response planning. Hydrological models, developed and tested over many years, will also examine the effects of varying levels of carp biomass on dissolved oxygen levels in a range of aquatic habitat types.

    These models will be complemented by detailed experimental studies in real ecosystems see Boros et al. Additional research may also explore nutrient interception pathways in freshwater ecosystems, identifying options for avoiding blue-green algae blooms.

    Together, these research projects will enable response planning that safeguards water quality. For further reading in these areas, Brookes et al. The need to phase any release and clean up strategy also presents some clear challenges. In particular, how to compartmentalise such a large, geographically, climatically and hydrologically diverse landscape.

    The aim of this program was to eradicate brown rat Rattus norvegicus from a km long, km wide sub-Antarctic island km east of the Falkland Islands through introduction of tonnes of poison over square miles km2. This knowledge enabled development of a staged program for implementation, in which the island was divided into a number of treatment zones, which were treated individually Figure 1. Using this staged, methodical strategy the project team were able to progressively move across the island, treating rats in each zone, testing effectiveness in each zones before moving on until eventually the entire island was treated successfully.

    This is a noteworthy accomplishment clearly considered impossible by some in Poncet et al. Glaciers enable South Georgia to be divided into discrete zones for the purpose of rodent control Figure reproduced from Poncet and Poncet, Under the National Carp Control Plan opportunities are being explored to utilise these assets to separate waters into discrete treatment zones, enabling carp to be treated within each zone in a staged manner.

    Dams and weirs present throughout the Murray-Darling Basin in green. Opportunities will be explored to use these compartmentalise reaches into zones, enabling progressive treatment for the control of carp source: Many Australian rivers are highly regulated, with locks, weirs, and dams controlling water movement Growns, The NCCP is working with river managers to identify ways that flows can be manipulated to assist release and clean-up and maintain water quality.

    Results from these research projects will show us what needs to be done. Expert help will then be enlisted to work out how we do it. The NCCP will form a Critical Issue Advisory Group composed of experts from areas including military and transport logistics, commercial carp harvesting, and large-scale human- and animal-health responses.

    These experts will develop detailed strategies for rapidly responding to carp mortality events, including identifying equipment and personnel needs. Live carp reduce water quality by stirring up mud as they feed and excreting nutrients into surrounding waters, which in turn promote blue-green algae blooms.

    Dead carp can also have impacts if left in a waterway. In sufficient numbers, dead carp can reduce oxygen levels in water, and as they decompose they can release nutrients into surrounding water, causing algal blooms and changes in water chemistry. Research proposed under the National Carp Control Plan will help to improve current understanding of how different quantities of dead carp impact on water quality in the variety of habitats that carp inhabit in Australia. Information collected will inform risk assessment and development of clean-up methods.

    Studies show that living carp muddy waters, increase nutrient levels thereby promoting blue-green algae blooms , and reduce abundance of water plants macrophytes , invertebrates e. Large organic matter inputs - including from dead fish - can result in low dissolved oxygen concentrations as microbes consume oxygen during respiration while decomposing the organic matter King et al.

    This is particularly true in shallow habitats with high carp biomass levels, as well as in high temperature or thermally-stratified environments Brookes, unpublished data, J. Large organic matter inputs are usually associated with flood events, during which vegetation litter is inundated and dissolved organic carbon DOC is leached from the substrate Whitworth et al.

    Information collected will inform risk assessment and development of clean up methods. Journal of Fish Biology , 43, Short-term effects of a prolonged blackwater event on aquatic fauna in the Murray River, Australia: Marine and Freshwater Research, 63, Marine and Freshwater Research , 59, Reviews in Fisheries Science and Aquaculture , 23, Ecological effects of common carp Cyprinus carpio in a semi-arid floodplain wetland. Reviews in Fisheries Science , 17, The effect of temperature on leaching and subsequent decomposition of dissolved carbon from inundated floodplain litter: Chemistry and Ecology , 30, The total amount of carp present in Australia, distribution of that biomass, and likely spread of the carp virus if released are all key areas of focus for research under the National Carp Control Plan.

    Options for phasing possible virus release will also be investigated under the NCCP research program, including use of barriers to fish migration dams and weirs to break large waterways into smaller units. If possible, this would enable carp to be treated within each discrete stretch of waterway in a staged manner. The NCCP is a process, not a forgone conclusion. However the total amount of carp present in Australia, distribution of that biomass, and likely spread of the Carp virus if released are all key areas of focus under the National Carp Control Plan.

    While possible, research being undertaken as part of the National Carp Control Plan will allow this risk to be better understood. A previous study Rakus et al. On this basis, it was thought that carp may seek out warm water refuges within Australian waterways, reducing the overall program effectiveness.

    Researchers are developing models to understand Australian waterways including water quality, flow and connectivity, how carp live and behave in those waterways, and how the carp virus impacts on carp populations. As part of this work, researchers will also consider the impact of any behavioural change in carp during infection, including identifying the presence of warm water refuges, where they might occur and the role they may play in reducing overall effectiveness of the program.

    On this basis they postulated that carp may seek out warmwater refuges within Australian waterways, in doing so reducing overall program effectiveness. This is a possibility, however is also being studied under the NCCP to enable this risk to be better understood.

    Researchers under the NCCP are conducting epidemiological modelling to better understand patterns of viral transmission, spread, and mortality. Epidemiological knowledge will also be required to predict the locations and environmental conditions in which major carp mortalities are likely, and equally, areas where sub-optimal outcomes may be experienced.

    The epidemiological modelling team is currently focussing on the crucial, and inter-related, roles that water temperature, carp physiological condition especially spawning-related stress , and carp density are likely to play in transmission and mortality.

    Research undertaken throughout the world tells us this is unlikely to occur. The carp virus is now found in 33 countries worldwide. It has not caused major ongoing fish kills in any of these countries, although recurrent kills in Lake Havasu, Arizona, have been anecdotally attributed to the carp virus. Researchers investigating presence of the carp virus in Japan sampled natural waterways.

    Not one experienced ongoing outbreaks. However, the National Carp Control Plan is committed to making its recommendations and decisions based on research undertaken in our own waterways. In particular, CSIRO scientists are currently working closely with the NCCP to model the epidemiology of the virus to predict carp population responses to different release scenarios, including likelihood of repeat outbreaks. Initial disease outbreaks in natural ecosystems can be significant, however there are very few examples of repeat outbreaks in a specific waterbody.

    Those few that have been reported point to low level mortalities following large initial carp kill events. Researchers investigating presence of Cyprinid herpesvirus 3 in natural waterways throughout Japan sampled waterways nationwide, and reported that none experienced recurrent outbreaks Minamoto et al.

    The few waterbodies where repeat outbreaks have been reported are largely artificial water bodies stocked with carp for recreational fishing, or Koi collections. Research that will be conducted under the National Carp Control Plan will further contribute to our understanding in this area. Epidemiological modelling will be used to predict carp population responses to different release scenarios, including likelihood of repeat outbreaks.

    Molecular comparison of isolates of an emerging fish pathogen, koi herpesvirus, and the effect of water temperature on mortality of experimentally infected koi. Detection and significance of koi herpesvirus KHV in freshwater environments. Nationwide Cyprinid Herpesvirus 3 in natural rivers of Japan. Research in Veterinary Science , 93, World Organisation for Animal Health. Response to mass mortality of carp: FAO fisheries proceedings, Journal of Fish Diseases , 33, The carp virus has now been found in 33 countries worldwide, and has not caused ongoing mass fish kills in any other country, suggesting the likelihood of ongoing outbreaks occurring is low.

    However, computer modelling undertaken under the NCCP research program may suggest there is value in re-treating specific areas for example, nursery habitats with the carp virus following initial release to deliver optimal results. Research proposed over the next 18 months will add to current understanding in this area. Both hypoxia and anoxia already occur within waterways as oxygen levels are dynamic and change with things like wind flow, velocity and high dissolved organic carbon.

    The research is aiming to predict the impact of carp mortality on the dissolved oxygen concentration of wetlands, rivers and floodplain habitats and whether water flow management can mitigate the risk. International examples suggest that it is unlikely that largescale ongoing outbreaks and anoxia events events would result. A study of prevalence of CyHV-3 in Japanese rivers reported that of rivers sampled, no repeat outbreaks were reported both before and after sampling took place in any rivers studied Minamoto et al.

    The few waterbodies where repeat outbreaks have been reported are largely artificially stocked water bodies for recreational fishing, or Koi populations. Based on lessons learnt from past use of viral biocontrol agents for invasive vertebrates, and on mathematical modeling, the carp virus will likely have the greatest impact in the first few years after release.

    After that, effectiveness may be diminished - but not lost - as virus and host adapt to each other. The release would therefore need to be complemented by secondary control measures to ensure enduring results.

    Genetic strategies are being carefully considered under the NCCP to work synergistically with the carp virus. These strategies would skew the sex ratio of the remaining carp population after release of the virus.

    As abundance of one sex diminished, so too would the whole population. New generations of more virulent, but still natural, strains of the carp virus may also be investigated. Of course, any strategy to manage carp impacts will be most effective if supported by efforts to promote ecosystem recovery through habitat restoration, native fish restocking, restoring native fish migration pathways, and addressing water quality concerns.

    The NCCP will be based on thorough and measured approaches, ensuring the benefits and risks of carp biocontrol are understood and the right recommendations are made to government in to ensure optimum outcomes for Australia. The team working on the National Carp Control Plan are delivering a comprehensive program of research, and consulting extensively with stakeholders and the community to inform development of an integrated plan to control carp in Australia.

    When and where might the virus be released? The NCCP is charged with developing a plan to reduce carp impacts at the national scale. Specifically, to assess the potential use of biocontrol. Local reductions in carp numbers are great, but have no real meaningful impact on river health at the continental scale. That's why we're focussing on developing a plan for Australia. Second, researchers have attempted to culture the carp virus on human cell lines, and cell lines of other primates i.

    In other words, even deliberate and concentrated attempts to infect human and other primate cells with the carp virus have been unsuccessful. People in thirty-three countries where carp virus is present have been repeatedly exposed to the carp virus without a single documented case of infection by the virus.

    This exposure has included clean-up from virus outbreaks, when workers have close, repeated contact with carp that are shedding large quantities of the virus. In addition infected fish are regularly eaten and the absence of infections under these conditions provides confidence that the virus is not transmissible to humans. There are multiple lines of evidence demonstrating that CyHV-3 will not infect humans: J ournal of Fish Diseases , 40, Apart from the fact that some Australian states prohibit the possession of carp, there has historically been relatively little interest in the species as a table-fish in Australia.

    However, there is no doubt that carp are seen as a useful food source by other nations, particularly those suffering from poor food security. We are investigating options for the wise use of carp biomass, irrespective of the control method used.

    Carp musters are great fun, and help to engage communities in pest control, however research demonstrates that angling events only reduce populations by approximately 0. Carp musters are great fun, and help to engage communities in pest control, however research demonstrates that this will not result in a lasting reduction in carp numbers Norris et al. For example, Norris et al. Similarly, in , anglers in the Goondiwindi Carp Cull removed 40 carp from Rainbow Lagoon, equivalent to 1.

    Models presented by Thresher and Brown and Walker demonstrate that unless carp populations can be a reduced by a large percentage, physical removal is unlikely to offer an effective method for carp control. On this basis, Gehrke et al.

    Roberts J and Tilzey R eds Controlling carp: Proceedings of a workshop 22—24 October , Albury. Carp are currently used to make fertilizer in Australia , and it may be possible to do so on a larger scale if the carp virus is used to reduce carp numbers and impacts.

    Researchers are exploring options for utilisation of carp biomass under the National Carp Control Plan. A wide range of options are being considered, including composting, conversion into fishmeal, and fertiliser.

    It is true that carp are worth money, however the concept of selling carp for profit is more complex than it sounds. Carp are one of the most farmed and consumed freshwater fish species worldwide. Because of this, the average global price of Carp is very low: This makes it extremely difficult to harvest, chill and export carp profitably.

    The project team wants to understand your local waterways, what's important about them and how you use them, and your concerns and questions so that they can be addressed in the plan. The NCCP team has been meeting regularly with communities members and interested groups across the carp distribution areas and we will be conducting an initial round of regional workshops and public meetings across the seven participating states and territories.

    These public information sessions will be held in the evening and give community members the opportunity to hear first-hand from the project team about the background, context and desired outcomes of the NCCP as well as the proposed approach towards its development.

    Importantly we will want to hear directly from community members about what is important to them. We simply don't have the resources to go to every town, but we are doing our best to consult with as many people as possible.

    There is a raft of ways you can have your say on the NCCP. The NCCP has partnered with natural resource management groups in each state and territory where carp exist to identify areas most affected by carp and the potential use of biocontrol, and focus on those. The current community consultation forums running from October to February are the first round of events, with another round of community consultation forums to occur from March-November You can also find out more about where the NCCP is up to by registering for our newsletter.

    Register your details at the bottom of our homepage to keep up to date on when we will be in your region. Are carp a symptom or a cause of environmental damage? Non-scientific Accordion content toggle.

    Scientific Accordion content toggle. Find out more about The Carp Problem. Experimental manipulations of the biomass of introduced carp Cyprinus carpio in billabongs.

    Impacts on water-column properties. Marine and Freshwater Research 48, — Experimental evidence from causal criteria analysis for the effects of common carp Cyprinus carpio on freshwater ecosystems: Reviews in Fisheries Science and Aquaculture 23, — Ecological effects of common carp C yprinus carpio in a semi-arid floodplain wetland.

    Marine and Freshwater Research 65, — Reviews in Fisheries Science 17, — How did carp get here? Slow beginnings Carp had a slow start in Australia, which is surprising given their wide distribution and high numbers today. The Boolarra strain appears Early introductions were followed by other releases, some involving up to 50, fish, through the ss. Perfect for on-the-go use, this is Who doesn't love the delicious, fruity taste of strawberries? This sweet, familiar flavor makes our Strawberry AK terpenes perfect for any occasion.

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