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Yellowtail - U.S.

Seriola rivoliana

Sometimes known as Almaco Jack, Hamachi, Kahala

This Species is Farm Raised

Summary

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.



CRITERIONPoints
Inherent Operational Risks1.25
Feed2.50
Pollution1.50
Risk to Other Species2.00
Ecological Effects2.50
Final Score 1.95
Color
Final ScoreColor
2.60 - 4.00
2.20 - 2.59
1.80 - 2.19
1.40 - 1.79
0.00 - 1.39

Inherent Operational Risks

Core Points (only one selection allowed)

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.

1.00This 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.

2.00This species is raised in a moderate risk system (e.g., most ponds; raceways; bottom culture of mollusks).

3.00This species is raised in a low risk system (e.g., re-circulating closed system; suspended culture of mollusks; zero-discharge ponds).

Points of Adjustment (multiple selections allowed)
-0.25Species is raised at a high stocking density; OR there is a high density of sites in the geographic region, with evidence of environmental impact.

-0.25Operations do not incorporate best-available, cost-effective technology to reduce environmental impact.

-0.25There are no effective zoning or permitting practices for siting of facilities.

-0.25Government 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).

+0.25Species 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).

+0.25Operations incorporate innovative culture methods that limit environmental impacts (e.g., polyculture).

+0.25There 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).

+0.25Government programs preferentially encourage the expansion of low-impact systems over high impact systems.


1.25Points for Inherent Operational Risks

Feed

Core Points (only one selection allowed)

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.

1.00Typical aquaculture feed includes high levels of fishmeal, fish oil, or "trash" fish (i.e., >20% of the feed; e.g., salmonid feeds).

2.00Typical 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).

3.00No 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).

Points of Adjustment (multiple selections allowed)
-0.25When fish products are used, the major sources score low on the Wild-Caught Fisheries Ranking System.

-0.25Feed contains greater than 10% of fish products and public or private sectors are not working to reduce fish content in feed.

-0.25Feed conversion ratio (FCR) is high (i.e., >2.0; e.g., eel).

-0.25Government 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.

+0.25When 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).

+0.25Feed 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).

+0.25Feed 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).

+0.25Government policy promotes research, development and commercialization of herbivorous species or other species not highly dependent on fishmeal.


2.50Points for Feed

Pollution

Core Points (only one selection allowed)

Typical effluent treatment procedures:

1.00Effluent is not treated before discharge (e.g., salmon net pens).

Effluent is not treated before discharge (KBWF, 2008).

2.00Effluent is partially treated before discharge (e.g., infrequently discharged effluent from catfish ponds).

3.00Effluent 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).

Points of Adjustment (multiple selections allowed)
-0.25Operations 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.

-0.25Pollutants (e.g., pesticides; parasiticides; antibiotics; plastic; nets; dead fish) are frequently discharged into the environment or otherwise not appropriately discarded.

-0.25Effluent regulations do not exist, are lax, or are poorly enforced, which allows for degradation of the aquatic environment.

-0.25Available 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.

+0.25Operations generally improve water quality or sediment/benthic characteristics (e.g., oyster farms).

+0.25Chemicals (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).

+0.25Robust 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).

+0.25Innovative 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.


1.50Points for Pollution

Risk to Other Species

Core Points (only one selection allowed)

Frequency and Impact of Escapes:

1.00Farmed 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).

2.00Escape 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).

3.00Farmed species never (or virtually never) escape to the wild (e.g., species is raised in bio-secure facilities).

Points of Adjustment (multiple selections allowed)
-0.25This 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).

-0.25This 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.

-0.25This 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).

Additionally, there is concern with similar farming operations in Australia that deformities in farmed Yellowtail caused by viral infections and insufficient feeding of juveniles may compromise the health of wild populations (Department of Fisheries, Western Australia, 2008). It is reasonable to assume that this would also be a possibility in U.S. waters.

-0.25Regulatory authorities are not adequately addressing the risks of escape or spread of disease associated with farming this species.

+0.25Rescore 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.

+0.25Operations 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.

+0.25Operations 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).

+0.25Regulatory authorities are addressing the risks of escape and spread of disease associated with farming this species.


2.00Points for Risk to Other Species

Ecological Effects

Core Points (only one selection allowed)

Ecological sensitivity of site used for operations:

1.00Operations are generally located in areas of high ecological sensitivity (e.g., coastal wetlands; mangroves).

2.00Operations 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).

3.00Operations 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).

Points of Adjustment (multiple selections allowed)
-0.25Farming 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.).

-0.25Harmful 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).

-0.25If 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).

-0.25Government policy encourages aquaculture operations to locate or expand in areas of high ecological sensitivity.

+0.25Operations enhance habitat structure or function (e.g., constructed wetlands).

+0.25Predator 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).

+0.25Seed 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).

+0.25Government 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).


2.50Points for Ecological Effects

Reference

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.

Fish Key

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.