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Yellow catfish

Tachysurus sinensis

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Distribution
no distribution map available
least concern



Information


Author: María J. Cabrera-Álvarez
Version: B | 1.3 (2022-09-18)


Reviewers: Pablo Arechavala-Lopez, Jenny Volstorf
Editor: Jenny Volstorf

Initial release: 2022-03-21
Version information:
  • Appearance: B
  • Last minor update: 2022-09-18

Cite as: »Cabrera-Álvarez, María J.. 2022. Tachysurus sinensis (WelfareCheck | farm). In: fair-fish database, ed. fair-fish. World Wide Web electronic publication. First published 2022-03-21. Version B | 1.3. https://fair-fish-database.net.«





WelfareScore | farm

Tachysurus sinensis
LiPoCe
Criteria
Home range
score-li
score-po
score-ce
Depth range
score-li
score-po
score-ce
Migration
score-li
score-po
score-ce
Reproduction
score-li
score-po
score-ce
Aggregation
score-li
score-po
score-ce
Aggression
score-li
score-po
score-ce
Substrate
score-li
score-po
score-ce
Stress
score-li
score-po
score-ce
Malformations
score-li
score-po
score-ce
Slaughter
score-li
score-po
score-ce


Legend

Condensed assessment of the species' likelihood and potential for good fish welfare in aquaculture, based on ethological findings for 10 crucial 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
  • Ce = Certainty of our findings in Likelihood and Potential

WelfareScore = Sum of criteria scoring "High" (max. 10)

score-legend
High
score-legend
Medium
score-legend
Low
score-legend
Unclear
score-legend
No findings



General remarks

Tachysurus sinensis is a nocturnal catfish that lives in China, Laos, Vietnam, Korea, Japan, India, and Russia and has been introduced in Germany. It is cultured mostly in China, but also in Southeast Asia, and is consumed in China and other Asian countries such as Japan and South Korea. T. sinensis reaches marketable size at 2 years (first year as fingerlings/juveniles, another 8 months of growth in the second year until market size). It is sometimes polycultured with Erythroculter ilishaeformis. Males grow 30% faster than females and reach bigger sizes, and so the farming industry tried to focus on creating a breed of only males. There are many types of breeding technologies available for this species: selective breeding of broodstock from natural waters, cross‐breeding with other species such as Pelteobagrus vachelli, cell and genetic engineering breeding (which generates an all-male breed), and molecular marker‐assisted breeding. However, there is little information available about their breeding behaviour, other than males provide parental care, and so natural breeding is not performed in farms. There is no information about migratory patterns, which could mean that there are none, however, further research is needed to confirm this hypothesis. There is also a lack of information about their social behaviour, including aggregation and aggressiveness, about the situations that cause them stress, and about the level of malformations found in farms. Stunning and slaughtering protocols are not developed yet for T. sinensis, but there are available high-standard methods for other catfish species that could be studied in T. sinensis. In general, more research needs to be carried out in order to establish the biological needs of T. sinensis.




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 unclear for minimal and high-standard farming conditions. Our conclusion is based on a low amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

LARVAE and FRY: WILD: no data found yet. FARM: ponds: ≥0.5-2.1 ha 1; cages 2 1 in lakes, rivers, and reservoirs 1: 25 m2 (5 x 5 m).

JUVENILES: WILD: no data found yet. FARM: ponds: ≥3-5 ha 1; in-pond raceways: 110 m2 (22 x 5 m) 3; cages 2 1 in lakes, rivers, and reservoirs 1: 25 m2 (5 x 5 m).

ADULTS: WILD: in rivers 4-5-6, lakes 7 4-5-6, channels 4-5-6 and large reservoirs 7. FARM: ponds 2 1: ≥3-5 ha 1; in-pond raceways: 110 m2 (22 x 5 m) 3; earthen ponds 8; cages 2 1 in lakes, rivers, and reservoirs 1: 25 m2 (5 x 5 m); pond polyculture 2 1; cage polyculture 1; culture-based fisheries 2; ponds with circulating water channels 1.

SPAWNERS: WILD: no data found yet. FARM: tanks: 500 L 9; indoor spawning pools: 4 m2 (2 x 2 m) 1.




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 high for minimal and high-standard farming conditions. Our conclusion is based on a medium amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

LARVAE and FRY: WILD: no data found yet. FARM: ponds: 0.2-0.3 m 1; cages: 2.5-3 m 1.

JUVENILES: WILD: DEMERSAL 10; 2.6 m 10. FARM: ponds: 1.5-2 m 1; cages: 2.5-3 m 1; in-pond raceways: 2 m 3.

ADULTS: WILD:  JUVENILES. FARM: ponds: 2-3 m 1; cages: 2.5-3 m 1; in-pond raceways: 2 m 3.

SPAWNERS: WILD: 0.2-1 m 11FARM: ponds: water level controlled 1; indoor spawning pools: 1.5 m 1.




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. It is high for high-standard farming conditions. Our conclusion is based on a low amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Resident 12 13.

All age classes: WILD: nocturnal (feeding) behaviour 7. Based on distribution ( General remarks), estimated 8-17 h PHOTOPERIOD, fresh water. FARM: for details of holding systems  crit. 1 and 2. LARVAE and FRY: high survival and growth in dark blue and black tanks, moderate stress and survival in white tanks, and high stress and low survival in green and maroon tanks 14.




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 theses circumstances?

It is low for minimal and high-standard farming conditions. Our conclusion is based on a medium amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

WILD: mature at age 1+ 15, although in some populations spawn at 0+ 5-15 and 2+ and 3+ 16-15. Spawns once a year 15. Spawning season April-August, with two spawning peaks: one in May and a smaller one in July-August 15. Water temperature: 23-30 °C 15. In simulated data: spawns in June-July during 3 days, in riverbeds, at 23-30 °C (optimal temperature: 22-25 °C) 11. Population sex ratio: 1.08 female:male 15. Group sex ratio: 1.14:1 female:male, which goes to 1.74 in spawning peak month 15. Sex ratio variation among populations 15. Male parental care 4-17. FARM: oxytocin injections to induce maturation 1. Hormonal manipulation to induce spawning 18-1 7 9, without stripping and with undisturbed fertilisation at sex ratio 1:1 or 1:1.5 female:male, stimulated by running water 1. Hormonal manipulation with female stripping at sex ratio 4:1 male:female 1, male testes removed, eggs and sperm mixed manually 1 7 9. Artificial incubation 1. Water temperature manipulation to promote earlier maturation 1. Males: ≥180 g; females: ≥120 g 1.




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. Our conclusion is based on a low amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

LARVAE and FRY: WILD no data found yet. FARM: cages: 2,000-3,000 IND/m1; ponds: 1.0-1.5 million IND/ha; soft-shelled turtle co-culture ponds: 3,000 IND/ha of 5g IND 2. High stocking densities 1.

JUVENILES: WILDno data found yet. FARM: cages: 1,000-1,500 IND/m1; soft-shelled turtle co-culture ponds: 3,000 IND/ha 2; in-pond raceways: 4.4 kg/m3 3; high stocking densities 1.

ADULTS: WILDno data found yet. FARM: cages: 500-600 IND/m1; soft-shelled turtle co-culture ponds: 3000 IND/ha 2; 10-15 IND/m2 1; in-pond raceways: 4.4 kg/m3 3; high stocking densities 1.

SPAWNERS: WILD: aggregations during spawning and nesting 4-5-6. FARM: no data found yet.




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?

There are no findings for minimal and high-standard farming conditions.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

LARVAE and FRY: WILD and FARM: no data found yet.

JUVENILES: WILD and FARM: no data found yet.

ADULTS: WILD and FARM: no data found yet.

SPAWNERS: WILD and FARM: no data found yet.




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. It is medium for high-standard farming conditions. Our conclusion is based on a medium amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

LARVAE and FRY: WILD: no data found yet. FARM: ponds with flat substrate 1, sediment thickness 15-30 cm 1; weed-free ponds and perimeter 1; crops can be planted on pond edges (1-1.5 m) to provide fish food and shelter 1

JUVENILES: WILD: DEMERSAL 1. Sand, gravel, rubble, preference for mud bottom with aquatic weed 7. Nutrient-rich clay sediment, with small herbaceous species 15. Prefer clear water but does well in muddy water 7FARM: ponds with flat substrate 1; weed-free ponds and perimeter 1.

ADULTS: WILD JUVENILES. FARM: weed-free ponds and perimeter 1; biological floating beds 1.

SPAWNERS: WILD: in riverbeds 11. Males make burrow nests on even river sandy shallow areas free or almost free from vegetation 19-20 and in clayey soil 4-6. FARM: spawning stimulation by slow water flow 1.




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 unclear for minimal and high-standard farming conditions. Our conclusion is based on a low amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

LARVAE and FRY: for stress and tank colour  crit. 3.

JUVENILES: no data found yet.

ADULTS: no data found yet.

SPAWNERS: no data found yet.




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?

There are no findings for minimal and high-standard farming conditions.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

LARVAE and FRY:no data found yet.

JUVENILES: no data found yet.

ADULTS: no data found yet.

SPAWNERS: no data found yet.




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. It is medium for high-standard farming conditions. Our conclusion is based on a low amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Common slaughter method: no stunning method available 21; by 2018 only available in the market as live fish 1; by 2018 there was no processing company in China 1. Further research needed to determine whether the situation has changed since then. High-standard slaughter method: for the related Clarias gariepinus, a) stunning with captive pistol (8 bar pressure) and chilling in icewater 22, b) dry electro-stunning (0.76 A, 150 V, AC+DC for 15 s) followed by chilling and decapitation 23 or c) freshwater electro-stunning (1.60 ± 0.11 A/dm2, 50 Hz, sinusoidal, A.C., conductivity of 876 μS) followed by chilling and decapitation 24. Further research needed to determine whether this applies to T. sinensis as well.




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 2 25, level 5 being 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: omnivorous 2 1; insectivorous 10. FARM: fish meal and fish oil may be partly* replaced by sustainable sources 26 27, but no data found yet for ADULTS and SPAWNERS.

partly = <51% – mostly = 51-99% – completely = 100%




Glossary


ADULTS = mature individuals, for details Findings 10.1 Ontogenetic development
DEMERSAL = living and feeding on or near the bottom of a body of water, mostly benthopelagic, some benthic
DOMESTICATION LEVEL 2 = part of the life cycle closed in captivity, also known as capture-based aquaculture 25
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, for details Findings 10.1 Ontogenetic development
IND = individuals
JUVENILES = fully developed but immature individuals, for details Findings 10.1 Ontogenetic development
LARVAE = hatching to mouth opening, for details Findings 10.1 Ontogenetic development
PHOTOPERIOD = duration of daylight
SPAWNERS = adults during the spawning season; in farms: adults that are kept as broodstock
WILD = setting in the wild



Bibliography


1 Li, Dapeng, Congxin Xie, Xugang He, Rong Tan, Xing Tian, Zhimin Zhang, and Yu Gao. 2018. The Success of Yellow Catfish Aquaculture in China: From Rare Wild Fish to Popular Farmed Fish. In Aquaculture in China, 270–282. John Wiley & Sons, Ltd. https://doi.org/10.1002/9781119120759.ch3_8.
2 Wang, Qidong, Lin Cheng, Jiashou Liu, Zhongjie Li, Shouqi Xie, and Sena S De Silva. 2014. Freshwater aquaculture in PR China: trends and prospects. Reviews in Aquaculture: 20.
3 Wang, Yuyu, Gangchun Xu, Zhijuan Nie, Nailin Shao, Quanjie Li, and Pao Xu. 2019. Growth Performance of Bluntnose Black Bream, Channel Catfish, Yellow Catfish, and Largemouth Bass Reared in the In-Pond Raceway Recirculating Culture System. North American Journal of Aquaculture 81: 153–159. https://doi.org/10.1002/naaq.10082.
4 Nikol’skii, G. V. 1954. Special Ichthyology. Journal of the Marine Biological Association of the United Kingdom 43: 279–280. https://doi.org/10.1017/S0025315400005439.
5 Liu, Shiping. 1997. A study on the biology of Pseudobagrus fulvidraco in Poyang Lake. CHINESE JOURNAL OF ZOOLOGY-PEKING- 32: 10–16.
6 Härtl, Michael, Michael Höllein, and Ulrich K Schliewen. 2018. First record of the East Asian Yellow Catfish Tachysurus fulvidraco (Richardson, 1846) in Germany. Spixiana 41: 167–168.
7 Weimin, Wang, Khalid ABBAS, and Yan Ansheng. 2006. Embryonic development of Pelteobagrus fulvidraco (Richardson, 1846). Chinese Journal of Oceanology and Limnology 24: 378–383. https://doi.org/10.1007/BF02842853.
8 Liu, Jin Yu, Ai Hua Li, Dong Ren Zhou, Zhou Rui Wen, and Xue Ping Ye. 2010. Isolation and characterization of Edwardsiella ictaluri strains as pathogens from diseased yellow catfish Pelteobagrus fulvidraco (Richardson) cultured in China. Aquaculture Research 41: 1835–1844. https://doi.org/10.1111/j.1365-2109.2010.02571.x.
9 Pan, Jianlin, Shuyan Ding, Jiachun Ge, Weihui Yan, Chen Hao, Jianxiu Chen, and Yahong Huang. 2008. Development of cryopreservation for maintaining yellow catfish Pelteobagrus fulvidraco sperm. Aquaculture 279: 173–176. https://doi.org/10.1016/j.aquaculture.2008.03.037.
10 Park, Tae-Jin, Moon-Kyung Kim, Seung-Hyun Lee, Young-Sun Lee, Mun-Ju Kim, Ha-Yoon Song, Ji-Hyoung Park, and Kyung-Duk Zoh. 2022. Occurrence and characteristics of microplastics in fish of the Han River, South Korea: Factors affecting microplastic abundance in fish. Environmental Research 206: 112647. https://doi.org/10.1016/j.envres.2021.112647.
11 Yang, Zefan, Peng Hu, Jianhua Wang, Yong Zhao, and Wenhai Zhang. 2019. Ecological flow process acknowledging different spawning patterns in the Songhua River. Ecological Engineering 132: 56–64. https://doi.org/10.1016/j.ecoleng.2018.12.034.
12 Chen, Daqing, Fei Xiong, Ke Wang, and Yonghua Chang. 2009. Status of research on Yangtze fish biology and fisheries. Environmental Biology of Fishes 85: 337–357. https://doi.org/10.1007/s10641-009-9517-0.
13 Zhou, Lei, Gongpei Wang, Tianxu Kuang, Dingli Guo, and Guifeng Li. 2019. Fish assemblage in the Pearl River Estuary: Spatial-seasonal variation, environmental influence and trends over the past three decades. Journal of Applied Ichthyology 35: 884–895. https://doi.org/10.1111/jai.13912.
14 Raghavan, Pichir, Zhu Xiao-Ming, Lei Wu, Han Dong, Yang Yun-Xia, and Xie Shou-Qi. 2013. Rearing tank color influences survival and growth of the early larvae of the yellow catfish, Pelteobagrus fulvidraco, Richardson. Acta Hydrobiologica Sinica 37: 177–184.
15 Cao, Ling, Biyu Song, Jinmiao Zha, Chengtai Yang, Xinfu Gong, Jianbin Li, and Weimin Wang. 2009. Age composition, growth, and reproductive biology of yellow catfish (Peltobagrus fulvidraco, Bagridae) in Ce Lake of Hubei Province, Central China. Edited by David L. G. Noakes, Aldemaro Romero, Yahui Zhao, and Yingqi Zhou. Environ Biol Fish 86. Developments in Environmental Biology of Fishes: 75–88. https://doi.org/10.1007/s10641-008-9342-x.
16 Zou, S. X., and B. P. Tian. 1998. Study on biology and fishery of Pelteobagrus fulvidraco in Taihu Lake. Journal of Sichuan Institute of Animal Husbandry and Veterinary Medicine 12: 36–41.
17 Watanabe, Katsutoshi. 2010. Mating Behavior and Larval Development of Pseudobagrus ichikawai.
18 Wang L., Chou Q., Zhou S., Liu H., Wu F. (1989). The biological characteristics, breeding and rearing of yellow catfish. Freshwater Fisheries, 6, 23–24. (in Chinese).
19 Kryzhanovskii, S. G., A. I. Smirnov, and S. G. Soin. 1951. Materials on Development of Fish of the Amur. Tr. Amurskoi ikhtiologicheskoi ekspeditsii 1945–1949 gg 2: 5–22.
20 Kasumyan, A. O. 2011. Tactile reception and behavior of fish. Journal of Ichthyology 51: 1035–1103. https://doi.org/10.1134/S003294521111004X.
21 Bowan, Jennifer, and Albin Gräns. 2019. Stunning and Killing of Tropical and Subtropical Finfish in Aquaculture during Slaughter.
22 Lambooij, E, R J Kloosterboer, C Pieterse, M A Gerritzen, and J W Van de vis. 2003. Stunning of farmed African catfish (Clarias gariepinus) using a captive needle pistol; assessment of welfare aspects. Aquaculture Research 34: 1353–1358. https://doi.org/10.1046/j.1365-2109.2003.00966.x.
23 Sattari, A., E. Lambooij, H. Sharifi, W. Abbink, H. Reimert, and J. W. van de Vis. 2010. Industrial dry electro-stunning followed by chilling and decapitation as a slaughter method in Claresse® (Heteroclarias sp.) and African catfish (Clarias gariepinus). Aquaculture 302: 100–105. https://doi.org/10.1016/j.aquaculture.2010.01.011.
24 Lambooij, E., R. J. Kloosterboer, M. A. Gerritzen, and J. W. van de Vis. 2006. Assessment of electrical stunning in fresh water of African Catfish (Clarias gariepinus) and chilling in ice water for loss of consciousness and sensibility. Aquaculture 254: 388–395. https://doi.org/10.1016/j.aquaculture.2005.10.027.
25 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.
26 Zhao, Zhen-xin, Chang-you Song, Jun Xie, Xian-ping Ge, Bo Liu, Si-lei Xia, Shun Yang, Qing Wang, and Sai-hua Zhu. 2016. Effects of fish meal replacement by soybean peptide on growth performance, digestive enzyme activities, and immune responses of yellow catfish Pelteobagrus fulvidraco. Fisheries Science 82: 665–673. https://doi.org/10.1007/s12562-016-0996-6.
27 Wang, Chunling, Lingli Jiang, Guoying Qian, and Youling Gao. 2017. Supplying rapeseed meal to the diets with or without potassium iodide for yellow catfish (Tachysurus fulvidraco). Aquaculture International 25: 2061–2078. https://doi.org/10.1007/s10499-017-0171-9.


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