Information
Authors: Caroline Marques Maia, Maria Filipa Castanheira
Version: C | 1.0Published: 2026-01-20
- profile update resulting in major editorial and content changes (changing the scoring in criteria 2-10)
- transfer to consistent age class and label structure resulting in changed appearance
- minor editorial changes plus new side note "Commercial relevance"
WelfareScore | farm
The score card gives our welfare assessments for aquatic species in 10 criteria.
For each criterion, we score the probability to experience good welfare under minimal farming conditions ("Likelihood") and under high-standard farming conditions ("Potential") representing the worst and best case scenario. The third dimension scores how certain we are of our assessments based on the number and quality of sources we found ("Certainty").
The WelfareScore sums just the "High" scores in each dimension. Although good welfare ("High") seems not possible in some criteria, there could be at least a potential improvement from low to medium welfare (indicated by ➚ and the number of criteria).
- Li = Likelihood that the individuals of the species experience good welfare under minimal farming conditions
- Po = Potential of the individuals of the species to experience good welfare under high-standard farming conditions
➚ = potential improvements not reaching "High" - Ce = Certainty of our findings in Likelihood and Potential
WelfareScore = Sum of criteria scoring "High" (max. 10 per dimension)
General remarks
Ctenopharyngodon idella is a freshwater carp found in riverbeds with strong currents that feeds on higher aquatic plants and submerged grasses, also taking detritus, insects, and other invertebrates. It naturally inhabits lakes, rivers, and reservoirs of Eastern China and Russia in eastern Siberia and the Amur River system. This species is one of the four Chinese major carps – together with Hypophthalmichthys molitrix, H. nobilis, and Mylopharyngodon piceus – and among the most important species cultured in inland water bodies in China. It is considered as a major farmed freshwater species in the world which has been introduced into more than 50 countries for aquaculture and aquatic weed control. Despite that, several countries report adverse ecological impact after introduction.
In aquaculture, this species is usually farmed in polycultures in ponds and pen and cage culture in lakes and reservoirs. Consumers appreciate this carp for its lack of fine inter-muscular bones. Farmers value some advantages for aquaculture, such as fast growth rate, large size, feeding habits, and tolerance of a wide range of temperatures, salinities, and oxygen levels. C. idella is susceptible to disease, though, and stressed by common farming procedures. Further research is needed on wild information related to depth, reproduction, and aggregation, besides aggression, malformations, and a slaughter protocol in farms. Carp welfare can be improved using pond culture systems promoting a natural habitat and behaviour of the species.
1 Home range
Many species traverse in a limited horizontal space (even if just for a certain period of time per year); the home range may be described as a species' understanding of its environment (i.e., its cognitive map) for the most important resources it needs access to.
What is the probability of providing the species' whole home range in captivity?
It is low for minimal farming conditions, as tanks, cages, and some ponds do not cover the higher end of the home range in the wild, although we cannot be sure in some age classes. It is high for high-standard farming conditions, as the range of other ponds covers the full home range in the wild. Our conclusion is based on a medium amount of evidence, as further research is needed on specific home range information in the wild.2 Depth range
Given the availability of resources (food, shelter) or the need to avoid predators, species spend their time within a certain depth range.
What is the probability of providing the species' whole depth range in captivity?
It is low for minimal farming conditions, as ponds, tanks, and cages do not cover the higher end of the depth range in the wild. It is medium for high-standard farming conditions, as the mentioned systems at least overlap with the range in the wild. Our conclusion is based on a medium amount of evidence, as further research is needed on specific depth information in the wild.3 Migration
Some species undergo seasonal changes of environments for different purposes (feeding, spawning, etc.), and to move there, they migrate for more or less extensive distances.
What is the probability of providing farming conditions that are compatible with the migrating or habitat-changing behaviour of the species?
It is low for minimal farming conditions, as the species undertakes more or less extensive migrations, and we cannot be sure that providing each age class with their respective environmental conditions will satisfy their urge to migrate or whether they need to experience the transition. It is medium for high-standard farming conditions, as the space range in captivity overlaps with the migration distance. Our conclusion is based on a high amount of evidence unless farm studies show that C. idella is well with shorter space range than in the wild.4 Reproduction
A species reproduces at a certain age, season, and sex ratio and possibly involving courtship rituals.
What is the probability of the species reproducing naturally in captivity without manipulation of these circumstances?
It is low for minimal farming conditions, as the species is manipulated (separation by sex, hormonal manipulation, stripping). It is medium for high-standard farming conditions, as omitting separation by sex and omitting stripping is verified for the farming context. Our conclusion is based on a medium amount of evidence, as further research is needed on age of maturity, mating type, and courting rituals in the wild as well as number of spawning events in captivity.5 Aggregation
Species differ in the way they co-exist with conspecifics or other species from being solitary to aggregating unstructured, casually roaming in shoals or closely coordinating in schools of varying densities.
What is the probability of providing farming conditions that are compatible with the aggregation behaviour of the species?
It is unclear for minimal and high-standard farming conditions, as the missing wild information on specific densities in schools or shoals does not allow a comparison with farming conditions. Our conclusion is based on a medium amount of evidence.6 Aggression
There is a range of adverse reactions in species, spanning from being relatively indifferent towards others to defending valuable resources (e.g., food, territory, mates) to actively attacking opponents.
What is the probability of the species being non-aggressive and non-territorial in captivity?
It is low for minimal farming conditions, as the species can be aggressive – even cannibalistic – under certain circumstances. It is high for high-standard farming conditions, as ways to reduce and in fact avoid aggression (sufficient feed, avoiding polyculture with certain species) are verified for the farming context. Our conclusion is based on a low amount of evidence, as further research is needed specifically addressing aggression (or lack thereof).7 Substrate
Depending on where in the water column the species lives, it differs in interacting with or relying on various substrates for feeding or covering purposes (e.g., plants, rocks and stones, sand and mud, turbidity).
What is the probability of providing the species' substrate and shelter needs in captivity?
It is low for minimal farming conditions, as almost all age classes of the species use substrate, but a) tanks and cages are devoid of it and b) given stripping in SPAWNERS. It is high for high-standard farming conditions given a) hatching substrate for eggs, b) earthen ponds for FRY to ADULTS which are not replaced by canvas or concrete bottom and enriched with bamboo mats, and given c) natural reproduction with spawning substrate in ponds for SPAWNERS. Our conclusion is based on a medium amount of evidence, as further research is needed to determine whether macrophytes are sufficient for FRY to ADULTS or whether they also benefit from enrichment with inundated vegetation like the SPAWNERS ponds.8 Stress
Farming involves subjecting the species to diverse procedures (e.g., handling, air exposure, short-term confinement, short-term crowding, transport), sudden parameter changes or repeated disturbances (e.g., husbandry, size-grading).
What is the probability of the species not being stressed?
It is low for minimal farming conditions, as the species is stressed (handling, confinement, high density, hyperthermia, stripping). It is medium for high-standard farming conditions, as some ways to reduce (but not avoid) stress are verified for the farming context, others need to be verified. Our conclusion is based on a medium amount of evidence, as further research is needed.9 Malformations
Deformities that – in contrast to diseases – are commonly irreversible may indicate sub-optimal rearing conditions (e.g., mechanical stress during hatching and rearing, environmental factors unless mentioned in crit. 3, aquatic pollutants, nutritional deficiencies) or a general incompatibility of the species with being farmed.
What is the probability of the species being malformed rarely?
It is low for minimal farming conditions, as malformation rates can exceed 10%. It is unclear for high-standard farming conditions, as some malformations are said to result from conditions that may be changed (diet, temperature, type of spawning induction), but improvements need to be verified for the farming context and the extent needs to be quantified. Our conclusion is based on a low amount of evidence, as further research is needed.10 Slaughter
The cornerstone for a humane treatment is that slaughter a) immediately follows stunning (i.e., while the individual is unconscious), b) happens according to a clear and reproducible set of instructions verified under farming conditions, and c) avoids pain, suffering, and distress.
What is the probability of the species being slaughtered according to a humane slaughter protocol?
It is low for minimal farming conditions (asphyxia). It is medium for high-standard farming conditions, as percussive stunning – followed by scaling, gutting, and filleting – or electrical plus percussive stunning – followed by exsanguination, evisceration, or destruction of the heart – induces unconsciousness fast (if done correctly) and kills while still unconscious but needs to be verified for C. idella. Our conclusion is based on a low amount of evidence, as further species-specific research is needed.Side note: Domestication
Teletchea and Fontaine introduced 5 domestication levels illustrating how far species are from having their life cycle closed in captivity without wild input, how long they have been reared in captivity, and whether breeding programmes are in place.
What is the species’ domestication level?
DOMESTICATION LEVEL 5 53, fully domesticated.
Side note: Forage fish in the feed
450-1,000 milliard wild-caught fishes end up being processed into fish meal and fish oil each year which contributes to overfishing and represents enormous suffering. There is a broad range of feeding types within species reared in captivity.
To what degree may fish meal and fish oil based on forage fish be replaced by non-forage fishery components (e.g., poultry blood meal) or sustainable sources (e.g., soybean cake)?
All age classes:
- WILD: herbivorous 54 2 37, feed mainly on higher aquatic plants and submerged terrestrial vegetation (during flooding) 3. LARVAE feed on zooplankton 3.
- FARM: can be reared with commercial feeds with sustainable sources (i.e. plant-based feed with no fish meal/fish oil) or with natural food, such as aquatic weeds and grasses 2 10. LARVAE feed on zooplankton, but feeding with artificial feed is also possible 3. Intensive feeding of ADULTS to become SPAWNERS with mixed feeds can cause serious functional disturbances (due to lack of green vegetation) that delay growth and maturation, also causing massive fish mortality 55↶3. SPAWNERS may be fed with fresh terrestrial plants 5. Fish meal may be partly* 56 or completely* 57 replaced by sustainable sources but affecting body composition 57. Fish oil may be completely* replaced by sustainable sources 58 59 without impairing growth but affecting body composition 59.
- LAB: diet without fish meal 31.
*partly = <51% – mostly = 51-99% – completely = 100%
Side note: Commercial relevance
How much is this species farmed annually?
5,728,383 t/year 1990-2019 amounting to estimated 1,263,000,000-5,728,000,000 IND/year 1990-2019 60.
Glossary
DOMESTICATION LEVEL 5 = selective breeding programmes are used focusing on specific goals 53
DPH = days post hatching
FARM = setting in farming environment or under conditions simulating farming environment in terms of size of facility or number of individuals
FRY = larvae from external feeding on
IND = individuals
JUVENILES = fully developed but immature individuals
LAB = setting in laboratory environment
LARVAE = hatching to mouth opening
NTU = Nephelometric Turbidity Units
PELAGIC = living independent of bottom and shore of a body of water
POTAMODROMOUS = migrating within fresh water
SPAWNERS = adults during the spawning season; in farms: adults that are kept as broodstock
WILD = setting in the wild
Bibliography
1 Xie, Congxin, Jiale Li, Dapeng Li, Yubang Shen, Yu Gao, and Zhimin Zhang. 2018. Grass Carp: The Fish that Feeds Half of China. In Aquaculture in China: Success stories and modern trends, 95–115. John Wiley & Sons, Ltd. https://doi.org/10.1002/9781119120759.ch3_6.
2 Weimin, M. 2009. Cultured Aquatic Species Fact Sheets. Ctenopharyngodon idellus. FAO.
3 Jeney, Z., and V. Bekh. 2020. Technical manual on broodstock management of common carp and Chinese herbivorous fish. Ankara, Turkey: Food and Agriculture Organization of the United Nations (FAO).
4 Jhingran, V.G., and R.S.V. Pullin. 1985. A hatchery manual for the common, Chinese and Indian major carps. Vol. 252. ICLARM Studies and Reviews 11. Asian Development Bank and International Center for Living Aquatic Resources Management.
5 Horvath, L., G. Tamas, A.G. Coche, E. Kovács, T. Moth-Poulsen, and A. Woynarovich. 2015. Training manual on the artificial propagation of carps. A handout for on-farm training workshops on artificial propagation of common carp and Chinese major carps in Central and Eastern Europe, the Caucasus and Central Asia. 978-92-5-108689–6. Food and Agriculture Organization of the United Nations.
6 Rottmann, Roger W., and Jerome V. Shireman. 1979. Tank spawning of grass carp. Aquaculture 17: 257–261. https://doi.org/10.1016/0044-8486(79)90129-7.
7 Hockin, D. C., K. O’Hara, and J. W. Eaton. 1989. A radiotelemetric study of the movements of grass carp in a British canal. Fisheries Research 7: 73–84. https://doi.org/10.1016/0165-7836(89)90008-8.
8 Bain, Mark B., David H. Webb, Michael D. Tangedal, and Larry N. Mangum. 1990. Movements and Habitat Use by Grass Carp in a Large Mainstream Reservoir. Transactions of the American Fisheries Society 119: 553–561. https://doi.org/10.1577/1548-8659(1990)119%3C0553:MAHUBG%3E2.3.CO;2.
9 Harris, C., T. O. Brenden, C. S. Vandergoot, M. D. Faust, S. J. Herbst, and C. C. Krueger. 2021. Tributary use and large-scale movements of grass carp in Lake Erie. Journal of Great Lakes Research 47: 48–58. https://doi.org/10.1016/j.jglr.2019.12.006.
10 Jha, S., S. Rai, M. Shrestha, J. S. Diana, R. B. Mandal, and H. Egna. 2018. Production of periphyton to enhance yield in polyculture ponds with carps and small indigenous species. Aquaculture Reports 9: 74–81. https://doi.org/10.1016/j.aqrep.2018.01.001.
11 Lu, J., S. Li, X. He, R. Tang, and D. Li. 2022. An in-pond tank culture system for high-intensive fish production: Effect of stocking density on growth of grass carp (Ctenopharyngodon idella Valenciennes, 1844) and blunt snout bream(Megalobrama amblycephala Yih, 1955). Aquaculture 549: 737808. https://doi.org/10.1016/j.aquaculture.2021.737808.
12 Szabó, T., B. Urbányi, T. Müller, R. Szabó, and L. Horváth. 2019. Assessment of induced breeding of major Chinese carps at a large-scale hatchery in Hungary. Aquaculture Reports 14: 100193. https://doi.org/10.1016/j.aqrep.2019.100193.
13 Shireman, J.V., and S.R. Smith. 1983. Synopsis of biological data on the grass carp Ctenopharyngodon idella (Cuvier and Valenciennes, 1844). 135. Centre for Aquatic Weeds University of Florida: Food and Agriculture Organization of the United Nations.
14 Shao, K. T., and P. L. Lim. 1991. Fishes of freshwater and estuary. Encyclopedia of field guide in Taiwan. Vol. 31. Taipei, Taiwan: Recreation Press, Co., Ltd.
15 Froese, R., and D. Pauly. 2014. FishBase. World Wide Web electronic publication. www.fishbase.org.
16 Hessler, T. M., D. C. Chapman, C. P. Paukert, J. C. Jolley, and M. E. Byrne. 2023. Winter Habitat Selection and Efficacy of Telemetry to Aid Grass Carp Removal Efforts in a Large Reservoir. North American Journal of Fisheries Management 43: 189–202. https://doi.org/10.1002/nafm.10693.
17 Nall, L. E., and et al. 1979. Radio telemetry tracking of the white amur in Lake Conway. Preliminary status report. Tallahassee, Florida: Bureau of Aquatic Plant Research and Control.
18 Riede, K. 2004. Global register of migratory species - from global to regional scales. Final report of the R&D Projekt 808 05 081. Bonn, Germany: Federal Agency for Nature Conservation.
19 Hessler, T. M., D. C. Chapman, C. P. Paukert, J. C. Jolley, and M. E. Byrne. 2023. Movement ecology of diploid and triploid grass carp in a large reservoir and upstream tributaries. PLOS ONE 18. Public Library of Science: e0281128. https://doi.org/10.1371/journal.pone.0281128.
20 Guillory, Vincent, and Robert D. Gasaway. 1978. Zoogeography of the Grass Carp in the United States. Transactions of the American Fisheries Society 107: 105–112. https://doi.org/10.1577/1548-8659(1978)107%3C105:ZOTGCI%3E2.0.CO;2.
21 Gorbach, E.I., and M.L. Krykhtin. 1988. Migration of the white amur, Ctenopharyngodon idella, and silver carp, Hypophthalmichthys molitrix, in the Amur River Basin. Journal Ichthyology 28: 47–53.
22 Gerrin, W. L., B. Haram, C. A. Jennings, G. Brandon, and S. B. Wilde. 2022. Factors affecting movement and habitat use of grass carp in a mainstem reservoir. Fisheries Management and Ecology 29: 100–103. https://doi.org/10.1111/fme.12517.
23 Weberg, M. A., B. R. Murphy, J. R. Copeland, and A. L. Rypel. 2020. Movement, habitat use, and survival of juvenile grass carp in an Appalachian reservoir. Environmental Biology of Fishes 103: 495–507. https://doi.org/10.1007/s10641-020-00953-0.
24 Culdmore, B, and N.E. Mandrak. 2004. Biological Synopsis of Grass Carp (Ctenopharyngodon idella). Canadian Manuscript Report of Fisheries and Aquatic Sciences: 44.
25 Raibley, P.T., K.D. Blodgett, and R.E. Sparks. 1995. Evidence of Grass Carp (Ctenopharyngodon idella) Reproduction in the Illinois and Upper Mississippi Rivers. Journal of Freshwater Ecology 10: 65–74. https://doi.org/10.1080/02705060.1995.9663418.
26 Liu, M., J. Lin, Q. Peng, L. Yu, D. Chen, S. Liu, and X. Duan. 2018. Relationship between the Distribution of Broodstock and Vorticity of Spawning Grounds of Four Major Chinese Carps in the Middle Reaches of the Yangtze River during Ecological Operation of the Three Gorges Dam. Water 10. Multidisciplinary Digital Publishing Institute: 1487. https://doi.org/10.3390/w10101487.
27 Federenko, A.Y., and F.J Fraser. 1978. Review of grass carp biology. Interagency Committee on Transplants and Introductions of Fish and Aquatic Invertebrates in British Columbia. 786. British Columbia, Department of Fisheries and Environment, Fisheries and Marine Service.
28 Stanley, Jon G., W. Woodard Miley, and David L. Sutton. 1978. Reproductive Requirements and Likelihood for Naturalization of Escaped Grass Carp in the United States. Transactions of the American Fisheries Society 107: 119–128. https://doi.org/10.1577/1548-8659(1978)107%3C119:RRALFN%3E2.0.CO;2.
29 De Silva, S., G. Turchini, and D. Francis. 2003. Aquaculture: Farming Aquatic Animals and Plants, 2nd Edition. In , 276–294. Oxford, UK: Blackwell Publishing.
30 Murtaza, Mahmood ul Hassan, Amina Zuberi, Muhammad Ahmad, Imrana Amir, Muhammad Kamran, and Manzoor Ahmad. 2020. Influence of early rearing environment on water-borne cortisol and expression of stress-related genes in grass carp (Ctenopharyngodon idella). Molecular Biology Reports 47: 5051–5060. https://doi.org/10.1007/s11033-020-05574-5.
31 Adineh, H., M. Naderi, A. Nazer, M. Yousefi, and E. Ahmadifar. 2021. Interactive effects of stocking density and dietary supplementation with Nano selenium and garlic extract on growth, feed utilization, digestive enzymes, stress responses, and antioxidant capacity of grass carp, Ctenopharyngodon idella. Journal of the World Aquaculture Society 52: 789–804. https://doi.org/10.1111/jwas.12747.
32 Buckley, B. R., and B. Stott. 1977. Grass Carp in a Sport Fishery. Aquaculture Research 8: 8–10. https://doi.org/10.1111/j.1365-2109.1977.tb00200.x.
33 George, A. E., D. C. Chapman, J. E. Deters, S. O. Erwin, and C.-A. Hayer. 2015. Effects of sediment burial on grass carp, Ctenopharyngodon idella (Valenciennes, 1844), eggs. Journal of Applied Ichthyology 31. John Wiley & Sons, Ltd: 1120–1126. https://doi.org/10.1111/jai.12918.
34 Van Dyke, J.M., A.J. Leslie Jr., and L.E. Nall. 1984. The effects of Grass Carp on the Aquatic Macrophytes of Four Florida Lakes. J Aquat Plant Manage 22: 87–97.
35 Opuszynski, K., and J.V. Shireman. 1995. Herbivorous Fishes: Culture and Use for Weed Management. Boca Raton, Florida: CRC Press.
36 Pípalová, I. 2006. A review of grass carp use for aquatic weed control and itsimpact on water bodies. J. Aquat. Plant Manage 44: 1–12.
37 Li, Xiangsong, Xiaoming Zhu, Dong Han, Yunxia Yang, Junyan Jin, and Shouqi Xie. 2016. Carbohydrate utilization by herbivorous and omnivorous freshwater fish species: a comparative study on gibel carp (Carassius auratus gibelio. var CAS III) and grass carp (Ctenopharyngodon idellus). Aquaculture Research 47: 128–139. https://doi.org/10.1111/are.12476.
38 Jiang, Danli, Yubo Wu, Di Huang, Xing Ren, and Yan Wang. 2017. Effect of blood glucose level on acute stress response of grass carp Ctenopharyngodon idella. Fish Physiology and Biochemistry 43: 1433–1442. https://doi.org/10.1007/s10695-017-0383-y.
39 Lin, W., L. Li, J. Chen, D. Li, J. Hou, H. Guo, and J. Shen. 2018. Long-term crowding stress causes compromised nonspecific immunity and increases apoptosis of spleen in grass carp (Ctenopharyngodon idella). Fish & Shellfish Immunology 80: 540–545. https://doi.org/10.1016/j.fsi.2018.06.050.
40 Faheem, M., S. Khaliq, R. Z. Abbas, and A. T. Mansour. 2022. Moringa oleifera alleviated oxidative stress, physiological and molecular disruption induced by acute thermal stress in grass carp, Ctenopharyngodon idella. Fish Physiology and Biochemistry 48: 1463–1473. https://doi.org/10.1007/s10695-022-01147-4.
41 Korwin-Kossakowski, M. 2008. The influence of temperature during the embryonic period on larval growth and development in carp, Cyprinus carpio L., and grass carp, Ctenopharyngodon idella (Val.): Theoretical and practical aspects. Archiwum Rybactwa Polskiego 16: 231–314.
42 Brzuska, E. 1999. Artificial spawning of herbivorous fish: use of an LHRH-a to induce ovulation in grass carp Ctenopharyngodon idella (Valenciennes) and silver carp Hypophthalmichthys molitrix (Valenciennes). Aquaculture Research 30: 849–856. https://doi.org/10.1046/j.1365-2109.1999.00413.x.
43 Varvara, Caterina, Edmond Hala, Mariasevera Di Comite, Rosa Zupa, Letizia Passantino, Gianluca Ventriglia, Angelo Quaranta, Aldo Corriero, and Chrysovalentinos Pousis. 2024. An Observational Study of Skeletal Malformations in Four Semi-Intensively Reared Carp Species. Veterinary Sciences 11. Multidisciplinary Digital Publishing Institute: 30. https://doi.org/10.3390/vetsci11010030.
44 Dabrowski, K., and P. Poczyczyński. 1988. Comparative experiments on starter diets for grass carp and common carp. Aquaculture 69: 317–332. https://doi.org/10.1016/0044-8486(88)90339-0.
45 Takeuchi, T., K Watanabe, W-Y Yong, and T. Watanabe. 1991. Essential fatty acids of grass carp Ctenopharyngodon idella. Nippon Suisan Gakkaishi. Published by The Japanese Society of Fisheries Science. 57: 467–473.
46 Takeuchi, T. 1996. Essential fatty acid requirements in carp. Archiv Fur Tierernahrung 49: 23–32.
47 Grimmett, S G, H J Chalmers, J C Wolf, and P R Bowser. 2011. Spinal deformity in triploid grass carp ctenopharyngodon idella (Valenciennes). Journal of Fish Diseases 34. John Wiley & Sons, Ltd: 217–225. https://doi.org/10.1111/j.1365-2761.2010.01229.x.
48 Zhang, L., Q. Li, J. Lyu, C. Kong, S. Song, and Y. Luo. 2016. The impact of stunning methods on stress conditions and quality of silver carp (Hypophthalmichthys molitrix) fillets stored at 4°C during 72h postmortem. Food chemistry 216: 130–137. https://doi.org/10.1016/j.foodchem.2016.08.004.
49 Zhang, L., Y. Zhang, S. Jia, Y. Li, Q. Li, K. Li, H. Hong, and Y. Luo. 2019. Stunning stress-induced textural softening in silver carp (Hypophthalmichthys molitrix) fillets and underlying mechanisms. Food Chemistry 295: 520–529. https://doi.org/10.1016/j.foodchem.2019.05.148.
50 Retter, Karina, Karl-Heinz Esser, Matthias Lüpke, John Hellmann, Dieter Steinhagen, and Verena Jung-Schroers. 2018. Stunning of common carp: Results from a field and a laboratory study. BMC Veterinary Research 14: 1–11. https://doi.org/10.1186/s12917-018-1530-0.
51 Rahmanifarah, K., B. Shabanpour, and A. Sattari. 2011. Effects of Clove Oil on Behavior and Flesh Quality of Common Carp (cyprinus Carpio L.) in Comparison with Pre-Slaughter Co2 Stunning, Chilling and Asphyxia. Turkish Journal of Fisheries and Aquatic Sciences 11: 139–147.
52 Qin, Na, Dapeng Li, Hui Hong, Yuemei Zhang, Beiwei Zhu, and Yongkang Luo. 2016. Effects of different stunning methods on the flesh quality of grass carp (Ctenopharyngodon idellus) fillets stored at 4 °C. Food Chemistry 201: 131–138. https://doi.org/10.1016/j.foodchem.2016.01.071.
53 Teletchea, Fabrice, and Pascal Fontaine. 2012. Levels of domestication in fish: implications for the sustainable future of aquaculture. Fish and Fisheries 15: 181–195. https://doi.org/10.1111/faf.12006.
54 Lin, D. 1991. Grass carp, Ctenopharyngodon idella. In Handbook of Nutrient Requirements of Finfish. In , 89–96. Boca Raton: FL: CRC Press.
55 Vinogradov, V. K., L. V. Erokhina, and A. S. Pisarenko. 1966. On use of combined feeds by grass carp when rearing it in ponds with common carp (in conditions of Moscow region) [in Russian]. Proc. VNIIPRkH: 15–24.
56 Cai, X., L. Luo, M. Xue, X. Wu, and W. Zhan. 2005. Growth performance, body composition and phosphorus availability of juvenile grass carp (Ctenopharyngodon idellus) as affected by diet processing and replacement of fishmeal by detoxified castor bean meal. Aquaculture Nutrition 11: 293–299. https://doi.org/10.1111/j.1365-2095.2005.00354.x.
57 Liang, X., X. Yu, J. Han, H. Yu, P. Chen, X. Wu, Y. Zheng, and M. Xue. 2019. Effects of dietary protein sources on growth performance and feed intake regulation of grass carp (Ctenopharyngodon idellus). Aquaculture 510: 216–224. https://doi.org/10.1016/j.aquaculture.2019.05.059.
58 Fletcher, Rob. 2017. Fish-free feed shortlist revealed. Fsh Farming Expert.
59 Liu, Yunlong, Yuan Yan, Zhen Han, Yancui Zheng, Xu Wang, Minying Zhang, Hongping Li, et al. 2022. Comparative effects of dietary soybean oil and fish oil on the growth performance, fatty acid composition and lipid metabolic signaling of grass carp, Ctenopharyngodon idella. Aquaculture reports 22: 101002. https://doi.org/10.1016/j.aqrep.2021.101002.
60 Mood, Alison, Elena Lara, Natasha K. Boyland, and Phil Brooke. 2023. Estimating global numbers of farmed fishes killed for food annually from 1990 to 2019. Animal Welfare 32. Cambridge University Press: e12. https://doi.org/10.1017/awf.2023.4.
The legend next to the WelfareScore card gives the definitions of the three dimensions we score the welfare of aquatic species on. You will also find the score options and how we arrive at the overall WelfareScore. If you scroll down to the criteria, you will find the explanations for the scores for each criterion for many species already. We are in the process of inserting these for all WelfareChecks we update. If your species of interest is missing these score justifications or if you are interested to know more details about the scoring procedure, please consult our scoring rationale.
For WelfareChecks we have not managed to update yet, previous scoring rationales may apply:
- before 2022: scoring rationale
- before 2018: scoring rationale
The criteria cover the main focus of the WelfareChecks – an assessment of the welfare of aquatic species. When selecting the criteria, though, we were aware of the importance of some topics so that we wanted to include them and collect data but not score them. For WelfareChecks | farm, these topics are "domestication level", "feed replacement", and "commercial relevance". The domestication and commercial relevance aspects allow us to analyse the questions whether increasing rate of domestication or relevance in farming worldwide goes hand in hand with better welfare; the feed replacement rather goes in the direction of added suffering for all those species which end up as feed. For a carnivorous species, to gain 1 kg of meat, you do not just kill this one individual but you have to take into account the meat that it was fed during its life in the form of fish meal and fish oil. In other words, carnivorous species (and to a degree also omnivorous ones) have a larger "fish in:fish out" ratio.
Probably, we updated the profile. Check the version number in the head of the page. For more information on the version, see the FAQ about this. Why do we update profiles? Not just do we want to include new research that has come out, but we are continuously developing the database itself. For example, we changed the structure of entries in criteria or we added explanations for scores in the WelfareCheck | farm. And we are always refining our scoring rules.
The centre of the Overview is an array of criteria covering basic features and behaviours of the species. Each of this information comes from our literature search on the species. If we researched a full Dossier on the species, probably all criteria in the Overview will be covered and thus filled. This was our way to go when we first set up the database.
Because Dossiers are time consuming to research, we switched to focusing on WelfareChecks. These are much shorter profiles covering just 10 criteria we deemed important when it comes to behaviour and welfare in aquaculture (and lately fisheries, too). Also, WelfareChecks contain the assessment of the welfare potential of a species which has become the main feature of the fair-fish database over time. Because WelfareChecks do not cover as many criteria as a Dossier, we don't have the information to fill all blanks in the Overview, as this information is "not investigated by us yet".
Our long-term goal is to go back to researching Dossiers for all species covered in the fair-fish database once we set up WelfareChecks for each of them. If you would like to support us financially with this, please get in touch at ffdb@fair-fish.net
See the question "What does "not investigated by us yet" mean?". In short, if we have not had a look in the literature - or in other words, if we have not investigated a criterion - we cannot know the data. If we have already checked the literature on a criterion and could not find anything, it is "no data found yet". You spotted a "no data found yet" where you know data exists? Get in touch with us at ffdb@fair-fish.net!
Once you have clicked on "show details", the entry for a criterion will unfold and display the summarised information we collected from the scientific literature – complete with the reference(s).
As reference style we chose "Springer Humanities (numeric, brackets)" which presents itself in the database as a number in a grey box. Mouse over the box to see the reference; click on it to jump to the bibliography at the bottom of the page. But what does "[x]↶[y]" refer to?
This is the way we mark secondary citations. In this case, we read reference "y", but not reference "x", and cite "x" as mentioned in "y". We try to avoid citing secondary references as best as possible and instead read the original source ourselves. Sometimes we have to resort to citing secondarily, though, when the original source is: a) very old or not (digitally) available for other reasons, b) in a language no one in the team understands. Seldomly, it also happens that we are running out of time on a profile and cannot afford to read the original. As mentioned, though, we try to avoid it, as citing mistakes may always happen (and we don't want to copy the mistake) and as misunderstandings may occur by interpreting the secondarily cited information incorrectly.
If you spot a secondary reference and would like to send us the original work, please contact us at ffdb@fair-fish.net
In general, we aim at giving a good representation of the literature published on the respective species and read as much as we can. We do have a time budget on each profile, though. This is around 80-100 hours for a WelfareCheck and around 300 hours for a Dossier. It might thus be that we simply did not come around to reading the paper.
It is also possible, though, that we did have to make a decision between several papers on the same topic. If there are too many papers on one issue than we manage to read in time, we have to select a sample. On certain topics that currently attract a lot of attention, it might be beneficial to opt for the more recent papers; on other topics, especially in basic research on behaviour in the wild, the older papers might be the go-to source.
And speaking of time: the paper you are missing from the profile might have come out after the profile was published. For the publication date, please check the head of the profile at "cite this profile". We currently update profiles every 6-7 years.
If your paper slipped through the cracks and you would like us to consider it, please get in touch at ffdb@fair-fish.net
This number, for example "C | 2.1 (2022-11-02)", contains 4 parts:
- "C" marks the appearance – the design level – of the profile part. In WelfareChecks | farm, appearance "C" is our most recent one with consistent age class and label (WILD, FARM, LAB) structure across all criteria.
- "2." marks the number of major releases within this appearance. Here, it is major release 2. Major releases include e.g. changes of the WelfareScore. Even if we just add one paper – if it changes the score for one or several criteria, we will mark this as a major update for the profile. With a change to a new appearance, the major release will be re-set to 1.
- ".1" marks the number of minor updates within this appearance. Here, it is minor update 1. With minor updates, we mean changes in formatting, grammar, orthography. It can also mean adding new papers, but if these papers only confirm the score and don't change it, it will be "minor" in our book. With a change to a new appearance, the minor update will be re-set to 0.
- "(2022-11-02)" is the date of the last change – be it the initial release of the part, a minor, or a major update. The nature of the changes you may find out in the changelog next to the version number.
If an Advice, for example, has an initial release date and then just a minor update date due to link corrections, it means that – apart from correcting links – the Advice has not been updated in a major way since its initial release. Please take this into account when consulting any part of the database.
First up, you will find answers to questions for the specific page you are on. Scrolling down in the FAQ window, there are also answers to more general questions. Explore our website and the other sub pages and find there the answers to questions relevant for those pages.
In the fair-fish database, when you have chosen a species (either by searching in the search bar or in the species tree), the landing page is an Overview, introducing the most important information to know about the species that we have come across during our literatures search, including common names, images, distribution, habitat and growth characteristics, swimming aspects, reproduction, social behaviour but also handling details. To dive deeper, visit the Dossier where we collect all available ethological findings (and more) on the most important aspects during the life course, both biologically and concerning the habitat. In contrast to the Overview, we present the findings in more detail citing the scientific references.
Depending on whether the species is farmed or wild caught, you will be interested in different branches of the database.
Farm branch
Founded in 2013, the farm branch of the fair-fish database focuses on farmed aquatic species.
Catch branch
Founded in 2022, the catch branch of the fair-fish database focuses on wild-caught aquatic species.
The heart of the farm branch of the fair-fish database is the welfare assessment – or WelfareCheck | farm – resulting in the WelfareScore | farm for each species. The WelfareCheck | farm is a condensed assessment of the species' likelihood and potential for good welfare in aquaculture, based on welfare-related findings for 10 crucial criteria (home range, depth range, migration, reproduction, aggregation, aggression, substrate, stress, malformations, slaughter).
For those species with a Dossier, we conclude to-be-preferred farming conditions in the Advice | farm. They are not meant to be as detailed as a rearing manual but instead, challenge current farming standards and often take the form of what not to do.
In parallel to farm, the main element of the catch branch of the fair-fish database is the welfare assessment – or WelfareCheck | catch – with the WelfareScore | catch for each species caught with a specific catching method. The WelfareCheck | catch, too, is a condensed assessment of the species' likelihood and potential for good welfare – or better yet avoidance of decrease of good welfare – this time in fisheries. We base this on findings on welfare hazards in 10 steps along the catching process (prospection, setting, catching, emersion, release from gear, bycatch avoidance, sorting, discarding, storing, slaughter).
In contrast to the farm profiles, in the catch branch we assess the welfare separately for each method that the focus species is caught with. In the case of a species exclusively caught with one method, there will be one WelfareCheck, whereas in other species, there will be as many WelfareChecks as there are methods to catch the species with.
Summarising our findings of all WelfareChecks | catch for one species in Advice | catch, we conclude which catching method is the least welfare threatening for this species and which changes to the gear or the catching process will potentially result in improvements of welfare.
Welfare of aquatic species is at the heart of the fair-fish database. In our definition of welfare, we follow Broom (1986): “The welfare of an individual is its state as regards its attempts to cope with its environment.” Thus, welfare may be perceived as a continuum on which an individual rates “good” or “poor” or everything in between.
We pursue what could be called a combination of not only a) valuing the freedom from injuries and stress (function-based approach) but b) supporting attempts to provide rewarding experiences and cognitive challenges (feelings-based approach) as well as c) arguing for enclosures that mimic the wild habitat as best as possible and allow for natural behaviour (nature-based approach).
Try mousing over the element you are interested in - oftentimes you will find explanations this way. If not, there will be FAQ on many of the sub-pages with answers to questions that apply to the respective sub-page. If your question is not among those, contact us at ffdb@fair-fish.net.
It's right here! We decided to re-name it to fair-fish database for several reasons. The database has grown beyond dealing purely with ethology, more towards welfare in general – and so much more. Also, the partners fair-fish and FishEthoGroup decided to re-organise their partnership. While maintaining our friendship, we also desire for greater independence. So, the name "fair-fish database" establishes it as a fair-fish endeavour.
