Yellowtail - U.S. |
|
Sometimes known as Almaco Jack, Hamachi, Kahala
This Species is Farm Raised
U.S. Yellowtail is farmed in net cages. Pollution concerns are generally low because cages are situated in areas of deeper water and strong currents, promoting the dispersal of waste. U.S. farmed Yellowtail are fed a diet containing moderate levels of fish meal and oil.
| CRITERION | Points |
|---|---|
| Inherent Operational Risks | 1.25 |
| Feed | 2.50 |
| Pollution | 1.50 |
| Risk to Other Species | 2.00 |
| Ecological Effects | 2.50 |
| Final Score | 1.95 |
| Color | ![]() |
| Final Score | Color |
|---|---|
| 2.60 - 4.00 | ![]() |
| 2.20 - 2.59 | ![]() |
| 1.80 - 2.19 | ![]() |
| 1.40 - 1.79 | ![]() |
| 0.00 - 1.39 | ![]() |
General System Design: An aquaculture system's design is a good overall proxy measure for the likely effect of the operation on the environment. For example, open systems (e.g., net pens and net cages) are more likely to have pollution, disease, and escape issues than closed systems (e.g., recirculating tanks). With shellfish, which don't require supplemental food input, the more important question is whether they are harvested on or off of the bottom.
| 1.00 | This species is raised in a high risk system (e.g., net pens; net cages). At the time of this assessment there was only one U.S. farm for Yellowtail, raising 500-700 tons per years of Yellowtail in six sea station net pens (KBWF, 2008). Yellowtail escapes from net pens were a concern during the initial stage of operation, but farming technology has since improved reducing the frequency of escapes. A score of 1 was awarded because some Yellowtail escapes still occur. |
| 2.00 | This species is raised in a moderate risk system (e.g., most ponds; raceways; bottom culture of mollusks). |
| 3.00 | This species is raised in a low risk system (e.g., re-circulating closed system; suspended culture of mollusks; zero-discharge ponds). |
| -0.25 | Species is raised at a high stocking density; OR there is a high density of sites in the geographic region, with evidence of environmental impact. | |
| -0.25 | Operations do not incorporate best-available, cost-effective technology to reduce environmental impact. | |
| -0.25 | There are no effective zoning or permitting practices for siting of facilities. | |
| -0.25 | Government programs encourage expansion of high-impact systems. NOAA, through the National Marine Aquaculture Initiative, encourages farming of marine finfish in near shore, open water, and terrestrial environments (NOAA, 2007). While funding is directed towards finding more sustainable farming methods, government policy does encourage expansion of high-impact net pens and cages (NOAA, 2007). | |
| +0.25 | Species is raised at a low stocking density OR there is a low density of sites in the geographic region, which results in minimal impact to the natural ecosystem. Species are raised at fairly low stocking densities of <30 kg per cubic meter (KBWF, 2008). Due to the low density of sites geographically and the relatively high current at the farm site (up to 2 knots) farm operations have had a minimal impact on water quality and benthic flora and fauna (Sarver, 2008). | |
| +0.25 | Operations incorporate innovative culture methods that limit environmental impacts (e.g., polyculture). | |
| +0.25 | There are effective zoning or permitting practices for siting and operation of facilities (e.g., mandatory consideration of hydrographic characteristics; requirements for site rotation). Currently, farming operations for yellowtail in Hawaii must undergo a comprehensive permitting process, including securing the following permits: a National Pollutant Discharge Elimination System (NPDES) Permit, a U.S. Department of the Army Permit, a Conservation District Use Application, a DOH Solid Waste Permit, and an Aquaculture License (KBWF, 2008). | |
| +0.25 | Government programs preferentially encourage the expansion of low-impact systems over high impact systems. | |
| 1.25 | Points for Inherent Operational Risks | |
Ecological Footprint of Feed: "Trash" fish, frequently used in developing countries, is an industry term used to refer to whole fish or fish parts fed to farmed fish without being processed into fish meal and fish oil. Twenty percent was selected as a cut-off because carnivorous species (e.g., salmon; eel; tuna; cobia; etc.) generally consume greater than twenty percent fish products (fishmeal, fish oil, or trash fish), while omnivorous or herbivorous species (e.g., catfish; tilapia; carps; etc.) consume less than twenty percent fish products.
| 1.00 | Typical aquaculture feed includes high levels of fishmeal, fish oil, or "trash" fish (i.e., >20% of the feed; e.g., salmonid feeds). |
| 2.00 | Typical aquaculture feed includes moderate levels of fishmeal, fish oil, or "trash" fish (i.e., <20% of the feed; e.g., tilapia and catfish feeds). U.S. Farmed Yellowtail is currently fed a diet around 20% fish meal and fish oil (Sims, 2008, personal communication). The majority of fish meal and oil is from targeted reduction fisheries, while a small amount is trimmings from the British Columbia hake fishery (Sims 2008, personal communication). |
| 3.00 | No feed is used (e.g., mollusks and seaweeds) or typical aquaculture feed includes no fishmeal, fish oil, or "trash" fish (e.g., paddlefish; filter-feeding carps). |
| -0.25 | When fish products are used, the major sources score low on the Wild-Caught Fisheries Ranking System. | |
| -0.25 | Feed contains greater than 10% of fish products and public or private sectors are not working to reduce fish content in feed. | |
| -0.25 | Feed conversion ratio (FCR) is high (i.e., >2.0; e.g., eel). | |
| -0.25 | Government policy promotes research, development and commercialization of carnivorous or other highly fishmeal-dependent species. NOAA, through the National Marine Aquaculture Initiative, encourages farming of carnivorous marine finfish in near shore, open water and terrestrial environments (NOAA, 2007). While grants are issued for research into alternative protein sources, encouraging farming of carnivorous finfish currently is highly dependent on fishmeal and oil. | |
| +0.25 | When fish products are used, the major sources score high on the Wild-Caught Fisheries Ranking System; OR the source is innovative and ecologically sound (e.g., fisheries byproducts); OR no feed is used. The majority of fish meal and oil is from the Peruvian anchovy fishery, a species that is abundant, grows quickly and has low vulnerability to fishing (Fishbase 2008). | |
| +0.25 | Feed contains less than 10% of fish products OR public and private sectors are working to reduce the fish content in feed; OR no feed is used. Both NOAA, through the National Marine Aquaculture Initiative grants program, and farmers of U.S. yellowtail are actively working to reduce the amount of fish content in feeds through grants for alternative proteins for feeds and feed trials (NOAA, 2007; Sims, 2008 personal communication). | |
| +0.25 | Feed conversion ratio (FCR) is low (i.e., <1.3; e.g., salmon); OR no feed is used. The 'wet-fish-in:wet-fish-out' ratio for U.S farmed yellowtail has improved recently and is now approximately 1.0 (Sims, 2008, personal communication). | |
| +0.25 | Government policy promotes research, development and commercialization of herbivorous species or other species not highly dependent on fishmeal. | |
| 2.50 | Points for Feed | |
Typical effluent treatment procedures:
| 1.00 | Effluent is not treated before discharge (e.g., salmon net pens). Effluent is not treated before discharge (KBWF, 2008). |
| 2.00 | Effluent is partially treated before discharge (e.g., infrequently discharged effluent from catfish ponds). |
| 3.00 | Effluent is substantially treated before discharge (e.g., recirculating shrimp systems; settling ponds; reconstructed wetlands); OR treatment is not necessary because supplemental feed is not used (e.g., molluscs or seaweeds). |
| -0.25 | Operations have demonstrated negative impacts on water quality or sediment/benthic characteristics (e.g., elevated nutrient levels; algal blooms; altered benthic communities). Nutrient levels, measured using total organic carbon, around the farm vary seasonally, being slightly higher in fall when ocean currents are weaker (Sarver, 2008). By winter, nutrient levels are low and similar to sites away from the farm. Benthic surveys around the farm show no to very little impact to the benthic community (Sarver, 2008). Because current farming operations cause no damage or negative impact to the local environment, no points were deducted. | |
| -0.25 | Pollutants (e.g., pesticides; parasiticides; antibiotics; plastic; nets; dead fish) are frequently discharged into the environment or otherwise not appropriately discarded. | |
| -0.25 | Effluent regulations do not exist, are lax, or are poorly enforced, which allows for degradation of the aquatic environment. | |
| -0.25 | Available technologies and practices to reduce or recycle waste (e.g., feed sensors; low-pollution feeds) are not used. Currently farming operations for Yellowtail in the U.S. do not use feed sensors or floating feeds, however most feedings are observed by divers and cameras to avoid overfeeding. Excess feed is said to be consumed by wild fish around the cages (KBWF, 2008). No points were deducted. | |
| +0.25 | Operations generally improve water quality or sediment/benthic characteristics (e.g., oyster farms). | |
| +0.25 | Chemicals (e.g., pesticides; parasiticides; antibiotics) are rarely or never used. Current U.S. Yellowtail farming operations use no prophylactic antibiotics. Florfenicol has been used several times to treat a specific bacterial infection under the supervisions of the US Fish and Wildlife Serve and veterinarians from the University of California, Davis (Sims, 2008, personal communication). | |
| +0.25 | Robust water quality regulations exist (e.g., permits required; discharge caps; strong enforcement), and regular monitoring occurs. U.S. Yellowtail farmers must conduct regular water quality monitoring to fulfill the EPA's National Pollutant Discharge Elimination System (NPDES) Permit (KBWF, 2008). Additionally, currently benthic flora and fauna is sampled quarterly to monitor impacts (Sarver, 2008). | |
| +0.25 | Innovative methods and practices to reduce or recycle wastes are used (e.g., integrated systems; effluent and solid wastes used as terrestrial fertilizer); OR innovative methods and practices are not needed because raising this species does not create waste. | |
| 1.50 | Points for Pollution | |
Frequency and Impact of Escapes:
| 1.00 | Farmed species regularly or intermittently escape into the wild AND escapes are non-native to the area or otherwise pose a risk to native populations or ecosystems (e.g., most non-native fish raised in outdoor facilities). |
| 2.00 | Escape frequency is not known OR farmed species is native to the area where it is raised and poses minimal risk to native populations or ecosystems (e.g., channel catfish in the US; most native mollusks). Escapes do occur, but Yellowtail is native to Hawaii (KBWF, 2008). At the beginning of farming operations tens of thousands of fish escaped (Sims, 2008, personal communication). Many small fish floated to the surface and were consumed by predators. Larger fish (3-4 kg), however, likely mixed with wild populations (Sims, 2008, personal communication). While escapes in farms have decreased with the use of Sea Station net pens, in December 2007, 1,500 fish escaped from Kona Blue's farm into surrounding waters when a diver failed to lock the bottom of the cage. Kona Blue is implementing procedures to ensure that this does not happen in the future (Honolulu Observer, 2008). |
| 3.00 | Farmed species never (or virtually never) escape to the wild (e.g., species is raised in bio-secure facilities). |
| -0.25 | This farmed species has been known to survive in the surrounding ecosystem if it escapes; OR would likely survive given its physiological requirements. While there is high predation of escapees by trevally, seals, dolphins and sharks, the species is native to the area (KBWF, 2008). While the impacts and survival rates of escapees are unknown, it is likely that escapees, if not predated, would survive in the wild (Sims, 2008, personal communication). | |
| -0.25 | This farmed species is known or is likely to compete with wild species for food or habitat if it escapes; OR this species is known or is likely to compromise the genetic integrity of the wild species (e.g., through spawning disruption, genetic introgression or establishment of feral stocks) if it escapes. Current farming operations do not selectively breed broodstock (KBWF, 2008). Also, broodstock are used for less than three generations (KBWF, 2008), thus there is little or no genetic difference between farmed and wild yellowtail. However, farmers are currently developing a selective breeding program to develop faster growing and more robust strains (KBWF, 2008). If these fish escape, they would likely breed with wild fish possibly altering the genetic make-up of wild populations. The farming operation will not begin culturing selected strains until net pen technology improves preventing fish escapes (KBWF, 2008), thus no points were subtracted. | |
| -0.25 | This farmed species is known or is likely to amplify and transmit disease or parasites to wild populations (e.g., infectious salmon anemia or sea lice infestations) if it escapes. Both foreign farmed and wild Yellowtail are very susceptible to viral infections, ciguatera and parasites (Hirayama et al., 2007; Perez-Arellano et al., 2005; KBWF, 2008). While low stocking densities are used in the U.S. and disease transfer may be less likely than in more high density operations in Japan and Australia, it is fair to assume that disease and parasite transmission are possible (KBWF, 2008). | |
| -0.25 | Regulatory authorities are not adequately addressing the risks of escape or spread of disease associated with farming this species. | |
| +0.25 | Rescore This farmed species has not been known to survive in the surrounding ecosystem if it escapes; OR would not likely survive given its physiological requirements; OR farmed species is a native mollusc. | |
| +0.25 | Operations employ management protocols and techniques to limit the ecological impacts of escaped farmed fish (e.g., triploidy; sterilization); OR it's unlikely that escaped individuals will either compete with wild species for resources, or compromise the genetic integrity of wild species. Current farming operations use either wild, first or second generation broodstock, so farmed fish are at most three generations removed from wild populations (KBWF, 2008). Current farming operations, therefore, are unlikely to compromise the genetic integrity of wild populations. | |
| +0.25 | Operations employ effective disease and parasite management protocols (e.g., fallowing of pens; retaining water when disease outbreak occurs); OR incidence of disease or risk of retransmitting disease is low. Indigences of disease outbreaks in existing farming operations is low and occasional treatment of cages with hydrogen peroxide prevents against outbreaks of parasites (Sims, 2008, personal communication). | |
| +0.25 | Regulatory authorities are addressing the risks of escape and spread of disease associated with farming this species. | |
| 2.00 | Points for Risk to Other Species | |
Ecological sensitivity of site used for operations:
| 1.00 | Operations are generally located in areas of high ecological sensitivity (e.g., coastal wetlands; mangroves). |
| 2.00 | Operations are generally located in areas of moderate ecological sensitivity (e.g., coastal and nearshore waters; rocky intertidal or subtidal zones; river or stream shorelines). Current operations are located about 0.5 miles from shore, with cages located in waters 200 ft deep (Sims, 2008, personal communication). The substrate under the farm is sand and thus not as high-risk as other habitats such as coral reefs (Sarver, 2008). |
| 3.00 | Operations are generally located in areas of low ecological sensitivity (e.g., land that is less susceptible to degradation such as land formerly used for agriculture or land previously developed). |
| -0.25 | Farming this species causes substantial damage to surrounding habitat, ecosystem or other resources (e.g., groundwater depletion; stream diversion; saltwater intrusion; soil salinization; loss of habitat for juvenile fish; loss of flood control; dredging hard bottoms; etc.). | |
| -0.25 | Harmful or lethal predator deterrents are used (e.g., bird/seal shootings; acoustic deterrent devices); OR operation otherwise harms wildlife (e.g., dolphin/seal entanglement; disrupting migration routes; bird/animal shooting). | |
| -0.25 | If seed is collected from wild sources, the intensity of collection is high enough to result in depletion of brood stock, wild juveniles, or associated non-target organisms (e.g., collection of postlarvae shrimp). | |
| -0.25 | Government policy encourages aquaculture operations to locate or expand in areas of high ecological sensitivity. | |
| +0.25 | Operations enhance habitat structure or function (e.g., constructed wetlands). | |
| +0.25 | Predator deterrents are not used OR predator deterrents are used but are not harmful or lethal (e.g., predator exclusion nets), AND operation does not otherwise harm wildlife. Existing farming operations do not employ any predator deterrents (Sims, 2008, personal communication). | |
| +0.25 | Seed comes predominantly from hatcheries or on-farm sites (e.g., seed for trout); OR if seed is collected from the wild, it does not deplete brood stock, wild juveniles, or associated non-target organisms (e.g., collection of oyster or mussel spat). About 50 wild Yellowtail are harvested annually from healthy wild populations and used as broodstock. Seed comes from these wild broodstock and does not deplete the wild population (KBWF, 2008). | |
| +0.25 | Government policy encourages the growth of aquaculture operations in areas of low ecological sensitivity; OR protects sensitive habitats from aquaculture operations (e.g., prohibitions on cutting mangroves). | |
| 2.50 | Points for Ecological Effects | |
Department of Fisheries, Western Australia. Accessed on 7-10-08. Yellowtail Kingfish ¨C An Emerging Industry. Available from: http://www.fish.wa.gov.au/wf/articles/YellowTailkingFish.php?0405
Fishbase. 2008. Anchoveta, Engraulis ringens: Available from: http://fishbase.com.
Hirayama T, Nagano I, Shinmoto H, Yagyu, KI and Oshima SI. 2007. Isolation and Characterization of Virulent Yellowtail Ascites Virus. Microbiology and Immunology. Vol. 51, No. 4. 397-406.
Honolulu Observer. January 18, 2008. Kona Blue may expand fish-farm business to Mexico¡¯s Sea of Cortez. Available from: http://the.honoluluadvertiser.com/article/2008/Jan/18/bz/hawaii801180337.html
Kona Blue Water Farms, LLC. 2008. Final Supplemental Environmental Assessment for an Expanded Production Capacity and Extended Farm Lease Area for Kona Blue¡¯s Offshore Open Ocean Fish Farm Project off Unualoha Point, Kona, Hawaii.
Masumoto T. Yellowtail, Seriola quinqueradiata. In Webster C, Lim C, eds. Nutrient Requirements and Feeding of Finfish for Aquaculture. CABI Publishing, Wallingford Oxon, UK. 448 pages
NOAA. 2007. Announcement of Federal Funding Opportunity: Executive Summary. Available from: http://aquaculture.noaa.gov/pdf/nmai08execsummary.pdf
Per¨¦z-Arellano J-L, Luzardo OP, Brito AP, Hern¨¢ndez Cabrera M, Zumbado M, Carranza C, et al. 2005. Ciguatera fish poisoning, Canary Islands. Emerging Infectious Diseases. Vol. 11, No. 12. Available from http://www.cdc.gov/ncidod/EID/vol11no12/05-0393.htm
Sarver, Dale. 2008. Benthic Sampling Report for Kona Blue Water Farms: Samples taken at the Offshore Farm site on: March 26, 2008. Deep Blue Research, LLC.
Sims, Niel, 2008. President of Kona Blue Waters Farms. Personal Communication on July 13, 2008.
![]() | Species is relatively abundant, and fishing/farming methods cause little damage to habitat and other wildlife. |
![]() | Species has medium to high levels of abundance, or fishing/farming methods cause some damage to the environment. |
![]() | Some problems exist with this species' status or catch/farming methods, or information is insufficient for evaluating. |
![]() | Species abundance is generally low, or fishing/farming methods typically have large environmental impact. |
![]() | Species has a combination of problems such as overfishing, high bycatch, and poor management; or farming methods have serious environmental impacts. |
| A fishery targeting this species has been certified as sustainable and well managed to the Marine Stewardship Council's environmental standard. Learn more at www.msc.org. | These fish contain levels of mercury or PCBs that may pose a health risk to adults and children. Please refer to http://www.edf.org/seafood for more details. |