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Nile tilapia

Oreochromis niloticus

Oreochromis niloticus (Nile tilapia)
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Distribution
Distribution map: Oreochromis niloticus (Nile tilapia)

least concern



Information


Authors: Jenny Volstorf, Caroline Marques Maia, João L. Saraiva
Version: C | 2.0 (2024-07-20)


Reviewer: Jenny Volstorf
Editor: Jenny Volstorf

Initial release: 2016-12-14
Version information:
  • Appearance: C
  • Last major update: 2024-07-20

Cite as: »Volstorf, Jenny, Caroline Marques Maia, and João L. Saraiva. 2024. Oreochromis niloticus (WelfareCheck | farm). In: fair-fish database, ed. fair-fish. World Wide Web electronic publication. First published 2016-12-14. Version C | 2.0. https://fair-fish-database.net.«





WelfareScore | farm

Oreochromis niloticus
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

Oreochromis niloticus originated in fresh waters of the Middle East as well as sub-Saharan Africa. It is one of the top 5 most frequently cultured species worldwide, mainly reared in Southeast Asia, China, and Africa. Due to its fast growth, it can reach market size in 5-6 months. Its rearing does not come without a toll on the individuals, though. Because maturity sets in early as well, farmers in intensive rearing administer hormones through the feed that renders individuals all male, or genetic engineering results in all-male populations. This prevents unwanted reproduction and the growth deficiencies that come with it. Also, it favours males which grow up to 50% faster than females.

The two most frequently used culture systems are ponds and cages of which earthen ponds, especially irrigation ponds or reservoirs, overlap more with the natural needs of space, density, and substrate than cages. Shelters and shading may also be applied artifically, though. IND are allowed to spawn naturally, i.e., without manipulation and stripping, but there seems to be a trend towards hormonal induction to synchronise spawning or avoid injuries by aggressive SPAWNERS. Aggression is an issue in other age classes as well and does not seem to be avoidable completely; one recommended method - to size grade - is stressful itself. Other husbandry practices like handling and transport impose stress, too, which may be reduced but not avoided. Electrical stunning followed by exsanguination, evisceration, or filleting is availabla but at risk of failing if not executed correctly.

Note: We used some older sources that referred to O. niloticus as Tilapia nilotica 1 2 or Sarotherodon niloticus 3 4 5 6, as was common at the time.




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, given we mainly found data from farms. Our conclusion is based on a medium amount of evidence, as further research is needed on home range in the wild.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs: does not apply.

LARVAE and FRY:

  • WILD: maternally mouthbred 1 7 (non-native habitat: 2 8 9). Mouthbreeding females release FRY 1 after yolk sac absorption, maximum 13.5 mm TOTAL LENGTH 10, guard over clouds of FRY 1, external feeding from 15 mm on 6. After female is gone, no data found yet on home range.
  • FARM: hatch in female’s mouth in breeding ponds (females leave when FRY reach 9-10 mm TOTAL LENGTH) 11 or are collected from female’s mouth 12 11 every 5-7 days 13 11, 10 days 14 to hatch in incubation jars 12 or 1-10 m3 nursery tanks 11 or 1-2 m2 15, 9-40 m2 (3 x 3 m, 8 x 2.5 m, 8 x 5 m) hapas in nursery ponds or directly in 100-500 m2 nursery ponds 11, 100-1,000 m2 16 or 200 m3 tanks 17. From incubation jars to pre-growing ponds: 30 m2 (3 x 10 m) 12. FINGERLINGS ponds: 200 m2 18. Pre-growing cages: 1 m2 (1 x 1 m) 19, 4 m2 (2 x 2 m) 20.
  • LAB: does not apply.

JUVENILES:

  • WILD: no data found yet.
  • FARM: ponds: 100-10,000 m2 21, 100 m2 22, minimum 300 m3 23, 660-6,600 m2 24, 5,000-14,000 m2 16, ponds for polyculture with C. gariepinus: 150 m2 25, irrigation ponds and reservoirs: <670,000 m2 24. Cages: 1-900 m2 (1 x 1 m, 30 x 30 m) 21, 1 m2 26, 2.3 m2 (1.5 x 1.5 m) 16, 3.1 m2 27, 4 m2 (2 x 2 m) 28 29, 6 m2 (3 x 2 m) 30, 9-18 m2 (3 x 3 m, 5-6 x 3 m) 11, 25 m2 (5 x 5 m) 24. Concrete tanks: 3.8 m2 (2.5 x 1.5 m) 31. Tanks and raceways: 10-1,000 m3, circular, rectangular, square, oval 32, tanks in RAS: 1.5 m3 33, tanks: 15 m2 34. Paddy fields 24.
  • LAB: does not apply.

ADULTS:

  • WILD: no data found yet.
  • FARM: JUVENILES.
  • LAB: does not apply.

SPAWNERS:

  • WILD: nests may be >1 m ∅ 1. Non-native habitat: bowers with pit of 0.4-1.9 m ∅ 35, nests of range 0.05-1 m ∅, mean 0.4-0.6 m ∅ 36. Mouthbreeding females stay inactive until FRY require external feed, then move to shallow areas 37 and guard FRY 1, external feeding from 15 mm on 6.
  • FARM: ponds: pre-spawning (sexes separated): 200 m2, then concrete (sexes combined, in hothouse): 24 m2 (4 x 6 m) 14, concrete: 30 m2 (3 x 10 m) 12, earthen ponds: 750 m2 15. Cages: 4.5 m2 (3 x 1.5 m) 19. Conditioning and production tanks: 24 m2 (3 x 8 m) 38, >30 m2 11, 200 m3 17. Higher number of eggs in 4 m2 (2 x 2 m) concrete tanks than 4 m2 (2 x 2 m) hapa nets 39. Hapa nets: 6 m2 (3 x 2 m) 40, 16 m2 (8 x 2 m) 13.
  • LAB: does not apply.



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, cages, tanks, and hapas do not cover the whole range in the wild (except for SPAWNERS). 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 high amount of evidence unless farm studies show that O. niloticus is well under lower depths as in the wild.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs:

  • WILD: maternally mouthbred 1 7 (non-native habitat: 2 8 9).
  • FARM: mouthbred 11 or collected from female’s mouth 12 11 every 5-7 days 13 11, 10 days 14 to hatch in jars and trays 11.
  • LAB: does not apply.

LARVAE and FRY:

  • WILD: maternally mouthbred 1 7 (non-native habitat: 2 8 9). Mouthbreeding females move to shallow areas 1 (non-native habitat: mouthbreeding females in 0-4 m littoral 8), release FRY 1 after yolk sac absorption, maximum 13.5 mm TOTAL LENGTH 10, guard over clouds of FRY 1, external feeding from 15 mm on 6. After female is gone, abundant in littoral <4 m 4, at 0.05-0.3 m during the day, deeper at night 6.
  • FARM: hatch in female’s mouth in breeding ponds (females leave when FRY reach 9-10 mm TOTAL LENGTH) 11 or are collected from female’s mouth 12 11 every 5-7 days 13 11, 10 days 14. Ponds: 0.5-1.4 m 16. Hapas in nursery ponds: 0.8-1.5 m 11, 1-2 m 15, increasing pond and hapa depth increases hatching rate and improves larval development through providing lower temperatures 11. FINGERLINGS ponds (until market size and beyond): higher growth and lower mortality at 3 m than 0.5, 1, or 2 m 18. Pre-growing cages: 1 m 19, 2 m 20.
  • LAB: does not apply.

JUVENILES:

  • WILD: caught at 0-4 m 3, ≤10 m, seldomly at 10-30 m 5; non-native habitat: caught at 0-4 m 8, ≤10 m 42, 0-15 m 43, at 12-16 m during day and night 44, some ≤20 m 43. Caught in lakes of 0.8-6.4 m 7, 2-4.9 m (non-native habitat: 45), 20 m (non-native habitat: 46-47) with unclear depth range use. Seldomly in open water and deeper depths at low turbidity 5, but also on the bottom in thick deposit of organic mud (non-native habitat: 44). Non-native habitat: moving between littoral with vegetation close to shore 8 and deeper off shore with sandy or rocky bottom 42; detritus in stomach indicates bottom grazing 45 48 49 50.
  • FARM: ponds: 0.5-3 m 21, 0.8 m at shallow end, 1.2 m at deep end 51 23, deeper (1-1.5) if entirely dependent on rain water 23, 1 m 22, 1 m at shallow end, 1.5-2 m at drainage end 11, 1.1-1.8 m 16, 1.5-3.5 m 24, ponds for polyculture with Clarias gariepinus: 1.3 m 25, irrigation ponds and reservoirs: >10 m 24. FINGERLINGS ponds (until market size and beyond): higher growth and lower mortality at 3 m than 0.5, 1, or 2 m 18. Cages: 0.8 m 29, 1 m 27 26, 1-3 m 21, 1.5 m 28 30 16, 3 m 11, 4-6 m 24. Concrete tanks: 1.1 m 31, tanks with bottom substrate: 1.2 m 34.
  • LAB: does not apply.

ADULTS:

  • WILD: JUVENILES.
  • FARM: JUVENILES.
  • LAB: does not apply.

SPAWNERS:

  • WILD: nests in 0.6-1.2 m 1. Non-native habitat: bowers with pit of 0.4-1.4 m depth, rim height of 0.01-0.5 m 35, nesting depth 0.8-1.4 m 36, mouthbreeding females in 0-4 m littoral 8.
  • FARM: ponds: pre-spawning (sexes separated): 1.2 m, then concrete (sexes combined, in hothouse): 1.5 m 14, concrete: 1 m, water level 0.7 m 12, earthen ponds: 0.5 m 15. FINGERLINGS ponds (until market size and beyond): breeding observed at 1, 2, and 3 m, but not at 0.5 m 18. Cages: 1 m 19. Hapa nets: 1 m 13 40, 1 m water level 39. Conditioning and production tanks: 0.8-0.9 m 11, 1 m 38, 1 m water level 39, deep tanks (1-2 m) increase reproductive performance 11.
  • LAB: does not apply.



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 medium amount of evidence, as further research is needed on specific migration distances in the wild.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Possibly POTAMODROMOUS 6. EURYHALINE, but grows best in fresh water 21.

Eggs: does not apply.

LARVAE and FRY:

  • WILD: maternally mouthbred in fresh7 (non-native habitat: 8) or brackish water 1 3 (non-native habitat: 9). Afterwards, abundant inshore 4, but present in all parts of the lake 6. Movement from one lake side to the opposite (lake breadth: 13-44 km), probably assisted by lake currents 6.
  • FARM: hatch in female’s mouth in breeding ponds (females leave when FRY reach 9-10 mm TOTAL LENGTH) 11 or are collected from female’s mouth 12 11 every 5-7 days 13 11, 10 days 14. For details of (freshwater) holding systems F1 and F2.
  • LAB: increasing morphological changes (yolk sac surface, lateral skeletal muscle, trunk area) with increasing salinity (0, 2, 4, 6 ppt) in newly-hatched LARVAE 52.

JUVENILES:

  • WILD: mainly in inshore waters of one (brackish) lake, sometimes moving offshore 1, in other lake: mostly open water 1, probably disperse after nursery phase into open waters 6. Non-native habitat: feeding at lake edges, in lagoons in estuaries of inflowing rivers, living off-shore in lakes 2, moving between littoral with vegetation close to shore and deeper off shore with sandy or rocky bottom 42.
  • FARM: for details of (freshwater) holding systems F1 and F2. May be transferred to <15 ppt in shallow seas, on beaches, in seaside ponds 24. Tanks: 2.7-4 g/L salinity 34.
  • LAB: no data found yet.

ADULTS:

  • WILD: JUVENILES.
  • FARM: JUVENILES.
  • LAB: no data found yet.

SPAWNERS:

  • WILD: fresh (non-native habitat: 8) or brackish water 1 3. If not already inshore, move there from open water to breed 1 6. Mouthbreeding females stay inactive until FRY require external feed, then move to shallow areas 37.
  • FARM: for details of (freshwater) holding systems F1 and F2.
  • LAB: no data found yet.



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 (hormonal manipulation, eggs taken from female’s mouth, in the lab also stripping) and may be taken from the wild. It is high for high-standard farming conditions, as natural breeding (without manipulation) with farm-reared IND is possible and verified for the farming context. Our conclusion is based on a medium amount of evidence, as further research is needed on reproduction behaviour in the wild.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs: does not apply.

LARVAE and FRY: does not apply.

JUVENILES: does not apply.

ADULTS: does not apply.

SPAWNERS:

  • WILD: mature in first year of life (non-native habitat: 8), spawn throughout the year 6 (non-native habitat: 8) every 30-90 days (non-native habitat: 9) in batches (non-native habitat: 53). Mouthbreeder: female takes eggs in mouth after fertilisation 1 6 7 (non-native habitat: 8 9) until after yolk sac absorption, maximum 13.5 mm TOTAL LENGTH 10, and guards them 1, external feeding from 15 mm on 6. For nest building  F3.
  • FARM: in Africa, IND may be taken from the wild 11. Mature at 5-6 months 11, used for spawning until 1.5-2 years 11 or at 2-4  years old 54, spawn every 21-90 days 39 19 at sex ratio 1:2 15 13 11, 1:3 19 12 14 11 40, or 1:4-1:10 male:female (tendency of higher number of eggs at 1:4) 39. PHOTOPERIOD and temperature adjustment to induce off-season spawning 38 which we do not consider manipulation. Hormonal manipulation for spawning induction to guarantee exact time of spawning 54. Male and female kept separately 14 54 11 for short time until ready to spawn which increases reproductive efficiency 11; 3 weeks after spawning, reconditioning period of 2 weeks during which IND are separated 13. Higher absolute number of eggs the heavier the female 15. Eggs are either left to hatch in female’s mouth in breeding ponds (females leave when FRY reach 9-10 mm TOTAL LENGTH) 11 or are collected from female’s mouth 12 11 every 5-7 days 13 11, 10 days 14, otherwise reduced reproductive potential and increased interspawning interval 11.
  • LAB: male courted female 55 56 57. Spawning only when visual or visual and chemical communication between male and female possible 57. Female released eggs in batches, took them immediately up in mouth 55. Males spawned 2-4 times/day, the higher the spawning frequency, the fewer eggs fertilised 58. The higher the female's age, weight, and length, the higher the total fecundity (number of eggs per spawn), the older the female, the higher the relative fecundity (number of eggs per kg weight) 58. Higher proportion of mouthbreeding under blue than under white light 59. Hormonal manipulation to induce spawning in females 60 61 54 62, plus artificial fertilisation (females 54 or both sexes stripped 60 62) to synchronise maturation for breeding programmes 60, to circumvent male aggression (injuries, mortality) during SPAWNERS pairings 62.



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 low for minimal farming conditions, as densities in ponds, cages, tanks, and hapas go beyond the smallest density in the wild. It is medium for high-standard farming conditions, as densities in other ponds at least overlap with the density range in the wild. Our conclusion is based on a high amount of evidence, unless farm studies show that O. niloticus is well under higher densities as in the wild.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs: does not apply.

LARVAE and FRY:

  • WILD: maternally mouthbred 1 7 (non-native habitat: 2 8 9). Mouthbreeding females release FRY 1 after yolk sac absorption, maximum 13.5 mm TOTAL LENGTH 10, guard over clouds of FRY 1, external feeding from 15 mm on 6. After female is gone, live in shoals 1 6 or schools (non-native habitat: 63). Estimated density in bed of Potamogeton pectinatus of IND 16-126 mm TOTAL LENGTH: 3.1 IND/m2 or 0.01 kg/m2 4. Non-native habitat: at 10-30 mm TOTAL LENGTH: 12-30 IND/m2 8.
  • FARM: hatch in female’s mouth in breeding ponds (females leave when FRY reach 9-10 mm TOTAL LENGTH) 11 or are collected from female’s mouth 12 11 every 5-7 days 13 11, 10 days 14. FRY: stocking in FINGERLINGS ponds: 10 IND/m2 11, nursery ponds: 100-200 IND/m2 11, 500 IND/m3 (concrete) 14, 1,000 IND/m2 16. Incubation systems: 5 IND/L, hapas in earthen ponds: 1,000-2,000 IND/m2 11. Higher growth in hapa nets with 250 IND/m2 than hapa nets with 1,000 IND/m2 and concrete tanks with 1,000 IND/m2 64. Cages: survival >75% at 1,000-3,000 IND/m3 for pre-growing IND to 2 months, decreasing survival at densities beyond that 19, 800 IND/m2 for pre-growing 2 months old IND to 5 months 19, higher growth of monosex male FINGERLINGS at 400 IND/m2 than 500 or 600 IND/m2 20.
  • LAB: no data found yet.

JUVENILES:

  • WILD: shoal when in open water 1. Estimated density in bed of Potamogeton pectinatus of IND 16-126 mm TOTAL LENGTH: 3.1 IND/m2 or 0.01 kg/m2 4, estimated density from bottom trawls: 0.00003 kg/m2 5. Non-native habitat: 0.001-0.01 IND/m2 given type of vegetation 8.
  • FARM: ponds: extensive: 1-2 IND/m2 21 (also for IND to become SPAWNERS) 11, semi-intensive: 1-2 IND/m2 (also for IND to become SPAWNERS) 11, 3-4 IND/m2 21, intensive: 3-3.8 IND/m2, in deep ponds with aeration 3.8-4.5 IND/m2, brackish water ponds 4.5-7.5 IND/m2, 5 IND/m2 11, 5-10 IND/m2 21, 8 IND/m2 65, 10-30 IND/m2 16, higher growth at 1 and 3 IND/m2 than 5 IND/m2 22, irrigation ponds and reservoirs: 0.8-1.5 IND/m2, at times with added Hypophthalmichthys molitrix, Hypophthalmichthys nobilis, Ctenopharyngodon idella, or Carassius carassius 24, polyculture possible with Penaeus vannamei in brackish ponds of overall density of 30-60 IND/m2 24. Ponds: higher growth and survival under 3:1 polyculture with Clarias gariepinus (intentionally stocked later to avoid preying on O. niloticus), specifically under 3 IND/m2 than 6 or 9 IND/m2 25. Cages: 10-15 IND/m3, up to 50-200 IND/m3 21, 20-50 IND/m3, 40-50 IND/m3 with good water quality and cooler water, otherwise 20 IND/m3 11, 50 IND/m3 26, 142-500 IND/m3 66, 267 IND/m2 16. Cages: higher growth at 100 than 150 or 200 IND/m3 27. Cages: higher growth and more uniform sizes during 41 days at 200 than 500, 625, or 750 IND/m2 making stressful size selection redundant and taking shorter to reach 800 g market size than medium-size selected IND at 150, 200, 225 IND/m2 28, higher growth at 375 than 525 and 675 IND/m2 30, higher growth and lower cortisol of genetically improved strain at 75 than 113 and 150 IND/m2 29. Concrete tank RAS and raceways: form shoal at 19.4 IND/m2 67, 10-50 IND/m2 11, no difference in growth between 16, 32, 42.6 IND/m2 31. Tanks in biofloc system: lower survival and water quality at 45 than 15 or 30 IND/m3 65. Tanks: 2 IND/m2 in monoculture, 0.5-2 IND/m2 in a polyculture with Penaeus vannamei of overall density of 4.5-11 IND/m2 34. Paddy fields: 0.5-0.6 IND/m2 24.
  • LAB: decreasing aggression with increasing density 68. Higher stress in groups of 10 IND than in singly-held IND or pairs, lower growth in groups of 5 or 10 IND, probably indicating crowding stress 69. 12-day old IND built shoal of 10-100 IND, 2-months-old IND built shoal of 27 IND 70. Higher growth and more aggressive behaviour at 100 and 200 IND/m3 than 400 IND/m3, even more growth but fewer aggressions (still keeping the difference between densities) when fed oregano essential oils at 1.0 or 2.0 mL/kg diet, higher frequency of “comfort behaviour” (chafing, resting, surfacing, elimination) at 100 than 200 or 400 IND/m3, no effect on schooling, increasing cortisol levels with increasing density 71. Tendency of higher growth at 0.6 than 1.2 kg/m3 in groups of 10 IND, unless high-density IND provided with tactile stimulation through vertical sticks with silicone bristles (although highest growth at low density plus stimulation) 72.

ADULTS:

  • WILD: shoal when in open water 1. Non-native habitat: 0.001-0.01 IND/m2 given type of vegetation 8.
  • FARM: JUVENILES.
  • LAB: no data found yet.

SPAWNERS:

  • WILD: spotted once: round shoals of several 100 IND with 3 m ∅, possibly in connection with breeding habit 1. Non-native habitat: bowers distributed in pond at 0.01-0.02 bowers/m2 35, nests aggregated in reservoir at 0.2-0.6 nests/m2 (the higher the turbidity the higher the nest density) 36. Mouthbreeding females form small groups until FRY require external feed, then separate to care for FRY individually 37.
  • FARM: higher frequency of spawning when stocked in compartments than in groups 11. Increasing aggression with increasing density 11. Ponds: for IND to become SPAWNERS: extensive: 1-2 IND/m2 11, semi-intensive: 1-2 IND/m2 11; pre-spawning ponds: 5 females/m2 14, optimally 4-6 IND/m2 11. Cages: 4 IND/m2 19. Conditioning and production tanks: 7-14 IND/m2 11, concrete tanks: increasing growth and number of eggs with decreasing stocking density (2.9, 3.2, 3.5 IND/m2) 38. Concrete tanks and hapa nets: tendency of highest number of eggs at 5 IND/m2 than 8 or 11 IND/m2 39.
  • LAB: 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?

It is low for minimal farming conditions, as the species is aggressive – even cannibalistic – in almost all age classes. It is medium for high-standard farming conditions, as a) ways to reduce (but not avoid) aggression (size homogeneity, density) are verified for the farming context, although there are contradictory findings on whether increasing or decreasing density is best and b) more ways to reduce aggression (adding oregano oil or tryptophan to the diet, tactile stimulation, low light intensity) need to be verified for the farming context. Our conclusion is based on a medium amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs: does not apply.

LARVAE and FRY:

  • WILD: maternally mouthbred 1 7 (non-native habitat: 2 8 9). Mouthbreeding females release FRY 1 after yolk sac absorption, maximum 13.5 mm TOTAL LENGTH 10, guard over clouds of FRY 1, external feeding from 15 mm on 6. After female is gone, live in shoals 1 6 or schools (non-native habitat: 63), thus probably no aggression.
  • FARM: hatch in female’s mouth in breeding ponds (females leave when FRY reach 9-10 mm TOTAL LENGTH) 11 or are collected from female’s mouth 12 11 every 5-7 days 13 11, 10 days 14. Leaving LARVAE to develop in breeding pond and scooping FRY may be difficult to get all IND out and because of cannibalism 24, cannibalism and predation by larger IND may be prevented by avoiding high stocking densities, by regular size grading, or by using double hapa which separates breeders from FRY 11. Stocking FRY of same age prevented cannibalism 19.
  • LAB: no data found yet.

JUVENILES:

  • WILD: no data found yet.
  • FARM: decreasing aggression with increasing density 73. No aggression reported in polyculture with Clarias gariepinus 25, Penaeus vannamei 34.
  • LAB: decreasing aggression with increasing density 68. Established linear hierarachy in groups of 4 males, dominant IND chased and attacked subordinate 74. Dominant IND displayed biting, ramming, cornering, chasing of subordinate IND and biting, ramming, mouth-fighting of other dominant IND in mixed-sex groups of 5, 10, or 15 IND 75, dominant IND chased and attacked subordinate 76 in mixed-sex pairs 77. Enrichment with river pebbles and plastic kelp increased number of fights and bites in pairs of IND compared to control 76. More aggressive behaviour at 100 and 200 IND/m3 than 400 IND/m3, fewer aggressions (but keeping the difference between densities) when fed oregano essential oils at 1.0 or 2.0 mL/kg diet 71. Lower number of bites against mirror in group of 10 IND when fed 2.6% tryptophan in diet than 1.3 than 0.3% 78, fewer confrontations when fed 2.6% tryptophan in diet than when provided shelters (PVC pipes) or artificial water hyacinth (frayed nylon rope) or control 79. Less aggressive behaviour and higher weight gain in groups of 4 IND when provided with tactile stimulation through vertical sticks with silicone bristles 80.

ADULTS:

  • WILD: no data found yet.
  • FARM JUVENILES.
  • LAB: in seven of 10 groups of two males 81, one male became dominant 82 81 56, chased and attacked subordinate IND 82. In six of seven groups of two males 81, larger male became resident over smaller male intruder 81 83, chased and attacked subordinate IND 81. Established linear hierarchy in groups of 3 females 84, 3 males 85, dominant IND chased and attacked subordinate 84 85. Tendency of fewer aggressions under low (280.8 lux) than high (1,394.1 lux) light intensity in group of 3 IND 85.

SPAWNERS:

  • WILD: no data found yet.
  • FARM: important to select IND of similar size, otherwise males 30-40% larger than females become very aggressive, nipping at females until the point of mortality 11. Increasing aggression with increasing density 11.
  • LAB: nesting male attacked other male 55. Established linear hierarchy in groups of 2 males:3 females, dominant males built nests and defended them against males and females 86. Nesting males released pulses (sounds) when another male entered the territory 87. Spawning only in dominant males in groups of 2 males and 3 females 86. Hormonal manipulation for spawning induction in females plus artificial fertilisation (both sexes stripped) to circumvent male aggression (injuries, mortality) during SPAWNERS pairings 62.



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 some ponds, cages, tanks, and hapas are devoid of it. It is high for high-standard farming conditions given a) eggs are left in female’s mouth, b) earthen ponds for FRY to ADULTS which are not replaced by concrete bottom, and given b) 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 shading and aerial protection nets suffice as replacements of structurally complex wetlands and macrophytes.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs:

  • WILD: maternally mouthbred 1 7 (non-native habitat: 2 8 9).
  • FARM: hatch in female’s mouth in breeding ponds (females leave when FRY reach 9-10 mm TOTAL LENGTH) 11 or are collected from female’s mouth 12 11 every 5-7 days 13 11, 10 days 14. Ponds: shading increases hatching rate through lower temperatures 11. For details of holding systems F1 and F2.
  • LAB: no data found yet.

LARVAE and FRY:

  • WILD: maternally mouthbred 1 7 (non-native habitat: 2 8 9), afterwards over sand (non-native habitat: 8) along shores or in muddy lagoons 1, in well-sheltered gulfs or bays 4, among inundated vegetation 6, seek shelter of macrophytes at night 6.
  • FARM: hatch in female’s mouth in breeding ponds (females leave when FRY reach 9-10 mm TOTAL LENGTH) 11 or are collected from female’s mouth 12 11 every 5-7 days 13 11, 10 days 14. Ponds: rocks or tarpaulin at the bottom (with or without aerial protection nets) 16, shading improves larval development through lower temperatures 11. For details of holding systems  F1 and F2.
  • LAB: no data found yet.

JUVENILES:

  • WILD: live along sheltered sandy beaches 1, in well-sheltered gulfs or bays 4, over sand and mud 7 (non-native habitat: 8 9 88). Seldomly in open water and deeper depths at low turbidity 5, but also on the bottom in thick deposit of organic mud (non-native habitat: 44). Non-native habitat: moving between littoral with vegetation close to shore 8 and deeper off shore with sandy or rocky bottom 42; detritus in stomach indicates bottom grazing 45 48 49 50; seek shelter from predatory Lates niloticus in complex wetlands 89-48 90-48 91-48 92-48; Secchi disc depth 0.2 m 45, 0.7-0.8 45 48. Higher abundance at lower transparency and higher abundance in structurally complex wetlands compared to open water might indicate taking shelter from Lates niloticus 48.
  • FARM: ponds: higher growth with added bamboo poles where periphyton grew than without substrate 51, minimal silt on bottom 24, substrate or rocks at the bottom, very turbid water 16. Cages: turbidity: Secchi disc 0.7-1.1 m 27. For details of holding systems F1 and F2.
  • LAB: enrichment with river pebbles and plastic kelp increased number of fights and bites in pairs of IND compared to control 76. Higher growth and lower scratching behaviour (stereotypical behaviour) when provided shelter (PVC pipes) or artificial water hyacinth (frayed nylon rope) than 2.6% tryptophan in diet (but no growth difference to control), preferred aquarium sections with shelters and artificial plant, lower ventilatory frequency with artificial plant 79. Longer time freezing during novel object test after 7 weeks isolation in barren than enriched aquaria (substrate) and than in 4 weeks isolation indicating fear, longer time exploring novel object after habituation in enriched than barren aquaria 93. Higher frequency of freezing, lower frequency of hovering and chasing in tanks 50% covered than open tanks, higher cortisol levels in 50% than 100% cover indicating disadvantages of 50% cover 94. Less aggressive behaviour and higher weight gain in groups of 4 IND when provided with tactile stimulation through vertical sticks with silicone bristles 80. Tendency of higher growth at 0.6 than 1.2 kg/m3 in groups of 10 IND, unless high-density IND provided with tactile stimulation through vertical sticks with silicone bristles (although highest growth at low density plus stimulation) 72.

ADULTS:

  • WILD: JUVENILES.
  • FARM: ponds: minimal silt on bottom 24. For details of holding systems F1 and F2.
  • LAB: males preferred aquaria with shelter over those without and aquaria with gravel over those without 95, in aquaria with shelter and gravel and bare bottom compartment, males preferred the gravel compartment on the first day and were indifferent between shelter, gravel, and bare bottom compartments on the following days 95.

SPAWNERS:

  • WILD: male builds nest in sand or inshore reed areas 1, in sandy sheltered conditions 6. Non-native habitat: bowers in sediment of mud and fine sand or silt and fine sand with 0-9.2 m distance to vegetation 35, nests in medium and fine sand at turbidity 3.1-11.3 NTU (the higher the turbidity the higher the nest density), sometimes covered by vegetation 36, mouthbreeding females in littoral with vegetation 8.
  • FARM: ponds: decreasing dissolved oxygen and temperature with increasing shading over hapa nets (no shading, shading on top, half, complete), higher absolute fecundity, spawning rate, number FRY under shading than without 40. Cages with solid base and 25 cm sand layer 19. Tanks: artificial spawning shelters improve reproductive efficiency 11. Hapa nets on tank bottom with mud 13. For details of holding systems F1 and F2.
  • LAB: males and females threw sand and cleaned the nest before spawning 55. Tanks: higher number of sexually active females when artificial reef installed than bare bottom, sandy bottom in between 96. Males and females built nests in aquaria with gravel layer 57. Males preferred aquaria with sand over aquaria with sand-shell mixture, did not nest in barren aquaria 97. Males moved larger mass for nest building and built wider nests under blue than white light 59. The higher the investment in nest building (weight of gravel displaced per body weight), the higher the spawning frequency and the more frequent female nest visits, but overall spawning frequency and latency independent of substrate indicating behavioural plasticity to reproduce under all kinds of circumstances 86.



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 (water quality, handling, confinement, crowding, transport). It is medium for high-standard farming conditions, as some ways to reduce (but not avoid) stress are verified for the farming context. Our conclusion is based on a high amount of evidence, as it seems clear that stress cannot be avoided.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs:

  • WILD: no data found yet.
  • FARM: stressed (to the point of mortality) when exposed to ≤17 °C or 39.5 °C directly after fertilisation, best hatching at 28 °C 58.
  • LAB: eggs hatched at a higher rate survived with higher probability in round-bottom than conical hatching jars, suggesting mechanical stress through friction between eggs and between eggs and container as major influence 58.

LARVAE and FRY:

  • WILD: no data found yet.
  • FARM: FRY: higher oxygen consumption and lower short-term growth after 6 h transport in polyethylene bags over bad road than over good road which might be improved through styrofoam pack absorbers 98. Stressed by handling in direct sunlight at noon, rather prefer handling in mornings or evenings and under shade 11, stressed by net material that will cause injuries, slightly larger mesh size that will entangle the gills, abrupt movements, dropping on the floor 11.
  • LAB: stressed by suppression of aeration (hypoxia), which may be reduced by the administration of sulfated polysaccharides (0.05-0.1 mg/g) in the feed (also improving growth) 17.

JUVENILES:

  • WILD: no data found yet.
  • FARM: stressed (to the point of mortality) by size grading 28. Cages: higher growth and lower cortisol of genetically improved strain at 75 than 113 and 150 IND/m2 29. Tanks in RAS: higher growth at 2,000 lux than 1,000 or 3,000 lux, lower cortisol at 18 and 24 h than 12 h PHOTOPERIOD 33. Stressed by transport for 4 h in plastic bags with oxygen at density 4 IND/L, even more so at 10 IND/L 99.
  • LAB: higher stress in groups of 10 than in singly-held IND or pairs, indicating crowding stress 69. Stressed by chasing with net for 60 s 69 100. Stressed by handling 101 102 which could not be reduced with eugenol but made handling IND easier 101, anaesthetisation with clove oil (250 m/L) more successive, but induced some stress itself 102. Stressed (to the point of mortality) under 24 h or 0 h PHOTOPERIOD compared to 12 h PHOTOPERIOD 103. No difference in ventilatory frequency under white, blue, or yellow light when tested individually 104. Higher cortisol levels in IND exposed to water from stressed conspecifics than in control group 100. Individual differences in boldness: males with more number of returns to and more time spent in former confinement area also displayed lower cortisol levels after emerged netting, faster food intake recovery in a novel environment, less neophobia towards a novel object, and more body displacements in an emerged net, indicating boldness 105; males escaping faster from a confinement situation also returned to the area the confinement took place slower, spent less time there, and displayed higher cortisol levels, indicating stress 105. Higher frequency of “comfort behaviour” (chafing, resting, surfacing, elimination) at 100 than 200 or 400 IND/m3, no effect on schooling, increasing cortisol levels with increasing density 71. Lower ventilatory frequency when provided with artificial water hyacinth (frayed nylon rope) than shelters (PVC pipes), 2.6% tryptophan in diet, or control 79. Higher cortisol levels in 50% than 100% cover indicating disadvantage of 50% cover 94.

ADULTS:

  • WILD: no data found yet.
  • FARM: no data found yet.
  • LAB: stressed by netting, even more so if done repeatedly 106. Probably stressed by food competition in group of 15 IND 107. No difference in growth under blue, violet, red, green, or yellow light when tested individually, but weight differences in groups of 4 IND except for yellow light with highest variation under red light 108. Stressed by confinement 109 plus white or green but not blue light 110 or more under white than blue light, yellow light in between 104. Auditory threshold 10 dB higher than control when exposed to noise for 28 days at 800 Hz 111. Stressed by tailfin clipping 112. Single IND stressed by pairing with dominant IND 113 or larger resident (increase in ventilatory frequency), confinement (either increase or decrease of ventilatory frequency), electric shock (either increase of decrease of ventilatory frequency) where the difference in ventilatory frequency reactions might indicate having to take a deeper look at this indicator, as it could also be the amplitude that is increasing 83.

SPAWNERS:

  • WILD: no data found yet.
  • FARM: extraction of eggs from mouth of female by lowering pond water level from 0.7 to 0.2 m, scooping out and placing on plate, which frightened female so that she released eggs 12.
  • LAB: 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?

It is high for minimal and high-standard farming conditions, as malformation rates do not exceed 10%. Our conclusion is based on a medium amount of evidence, as further research is needed.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs:

  • WILD: no data found yet.
  • FARM: no data found yet.
  • LAB: no data found yet.

LARVAE and FRY:

  • WILD: no data found yet.
  • FARM: deformities in 3.3-8.3% of IND, with no effect of amount of inbreeding 114.
  • LAB: increasing morphological changes (yolk sac surface, lateral skeletal muscle, trunk area) with increasing salinity (0, 2, 4, 6 ppt) in newly-hatched LARVAE 52.

JUVENILES:

  • WILD: no data found yet.
  • FARM: skeletal deformities (lateral projections of the mandible, 'parrot-like head', scoliosis, kyphosis, lordosis, fusion of dorsal and anal fins) in 1.6-2.7% 115.
  • LAB: no data found yet.

ADULTS:

  • WILD: no data found yet.
  • FARM: JUVENILES.
  • LAB: no data found yet.

SPAWNERS:

  • WILD: no data found yet.
  • FARM: no data found yet.
  • LAB: 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 high for high-standard farming conditions, as electrical stunning, followed by exsanguination, evisceration, or filleting, induces unconsciousness fast (if done correctly), kills while still unconscious, and is verified for the farming context. Our conclusion is based on a medium amount of evidence, as further research is needed to determine how often electrical stunning fails in the farming context.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs: does not apply.

LARVAE and FRY: does not apply.

JUVENILES:

  • WILD: does not apply.
  • FARM: minimal slaughter method: sold alive 24 at local markets without ice 23 to postpone rigor mortis 11, so probably asphyxia; placing on ice or in refrigerator 23 11, so probably asphyxia. Electrical stunner used in an inappropriate way and without amperage control, not followed by slaughter step resulting in IND receiving improper electrical shocks and being peeled and filleted alive 16. High-standard slaughter method: rapid killing (unspecified) followed by gutting or filleting 23, in-water electrical stunning followed by bleeding 116.
  • LAB: no data found yet.

ADULTS:

  • WILD: does not apply.
  • FARM: probably JUVENILES, but sources do not specify the age class 117.
  • LAB: electrical stunning 118. Fastest time to loss of vital signs under electrical stunning than immersion in 50:50 ice water mixture or CO2 narcosis, higher cortisol levels under 50:50 ice water mixture although still considered low stress 119. Higher number of IND losing consciousness without recovery after lateral than frontal spiking with Ikigun 120. Electrical stunning in water did not render IND unconscious 120. Faster onset of unconsciousness by mechanical spiking with captive bolt pistol than anaesthesia with 2-phenoxyethanol, essential oils (Ocimum americanum or Lippia alba), or hypothermia in 1:2 water:ice mixture, but a) IND did not show aversion to the essential oils rendering them nonetheless interesting for stunning, b) hypothermia caused irregular heart beat indicating stress, 4/5 IND regained consciousness, spectral analyses questioned whether unconsciousness was actually achieved, and c) spiking required expertise to execute effectively, otherwise in >60% of IND unconsciousness was not induced 120.

SPAWNERS:

  • WILD: does not apply.
  • FARM: no data found yet.
  • LAB: no data found yet.



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 5 121, 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: opportunistic – either mainly herbivorous 6 (non-native habitat: 45 44 49 122 88) or mainly omnivorous (non-native habitat: 8 48 43 50).
  • FARM: fish meal may be completely* replaced by non-forage fishery components 123. Ponds: no external feed administered in extensive culture systems 11. Cages: feed without fish meal and fish oil 26. Higher growth of SPAWNERS in fertilised than unfertilised ponds, higher number of hatched FRY at 25-30% protein level for SPAWNERS in pre-spawning period 14.
  • LAB: fish meal may be completely* replaced be some sustainable sources 124, not 125 126, partly* 127, or mostly* replaced by other sustainable sources 128. Fish meal may be partly* replaced by non-forage fishery components 129 130. Fish oil may be completely* replaced by some sustainable sources 131 132, partly* by other sustainable sources 133.

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




Glossary


ADULTS = mature individuals
DOMESTICATION LEVEL 5 = selective breeding programmes are used focusing on specific goals 121
EURYHALINE = tolerant of a wide range of salinities
FARM = setting in farming environment or under conditions simulating farming environment in terms of size of facility or number of individuals
FINGERLINGS = early juveniles with fully developed scales and working fins, the size of a human finger
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
PHOTOPERIOD = duration of daylight
POTAMODROMOUS = migrating within fresh water
RAS = Recirculating Aquaculture System - almost completely closed system using filters to clean and recirculate water with the aim of reducing water input and with the advantage of enabling close control of environmental parameters to maintain high water quality
SPAWNERS = adults during the spawning season; in farms: adults that are kept as broodstock
TOTAL LENGTH = from snout to tip of caudal fin as compared to fork length (which measures from snout to fork of caudal fin) or standard length (from head to base of tail fin) or body length (from the base of the eye notch to the posterior end of the telson) 41
WILD = setting in the wild



Bibliography


1 Worthington, E. B., and C. K. Ricardo. 1936. Scientific results of the Cambridge Expedition to the East African Lakes, 1930-1.—No. 15. The fish of Lake Rudolf and Lake Baringo. Zoological Journal of the Linnean Society 39: 353–389. https://doi.org/10.1111/j.1096-3642.1936.tb00472.x.
2 Lowe-McConnell, Rosemary H. 1959. Breeding behaviour patterns and ecological differences between tilapia species and their significance for evolution within the genus tilapia (Pisces: Cichlidae). Proceedings of the Zoological Society of London 132: 1–30. https://doi.org/10.1111/j.1469-7998.1959.tb05510.x.
3 Hopson, A. J., and J. Hopson. 1982. The fishes of Lake Turkana. In A report on the findings of the Lake Turkana project 1972-1975, ed. A. J. Hopson, 1:281–348. London: Overseas Development Administration.
4 Hopson, A. J., B. J. Harbott, and A. A. Q. R McLeod. 1982. Shore survey. In A report on the findings of the Lake Turkana project 1972-1975, ed. A. J. Hopson, 2:557–580. London: Overseas Development Administration.
5 Hopson, A. J., J. Hopson, A. A. Q. R McLeod, and M. G. Pawson. 1982. Openwater surveys. In A report on the findings of the Lake Turkana project 1972-1975, ed. A. J. Hopson, 2:581–750. London: Overseas Development Administration.
6 Hopson, A. J., A. A. Q. R McLeod, B. J. Harbott, and J. T. N. Ogari. 1982. The biology of perciform fishes. In A report on the findings of the Lake Turkana project 1972-1975, ed. A. J. Hopson, 5:1283–1502. London: Overseas Development Administration.
7 Komolafe, O. O., and G. a. O. Arawomo. 2007. Reproductive strategy of Oreochromis niloticus (Pisces: Cichlidae) in Opa reservoir, Ile-Ife, Nigeria. Revista de Biología Tropical 55: 595–602.
8 Balirwa, J. S. 1998. Lake Victoria wetlands and the ecology of the Nile tilapia, Oreochromis niloticus Linne. Ph.D.  dissertation, Wageningen, The Netherlands: Wageningen Agricultural University.
9 Peterson, Mark S., William T. Slack, Nancy J. Brown-Peterson, Jennifer L. McDonald, and C. M. Taylor. 2004. Reproduction in Nonnative Environments: Establishment of Nile Tilapia, Oreochromis niloticus, in Coastal Mississippi Watersheds. Copeia 2004: 842–849. https://doi.org/10.1643/CE-04-134R1.
10 Lowe (McConnell), Rosemary H. 1955. The Feduncity of Tilapia Species. The East African Agricultural Journal 21: 45–52.
11 Salin, Krishna R., and Amara Yakupitiyage. 2023. A manual for Nile tilapia seed production and grow-out aquaculture. Penang, Malaysia: WorldFish.
12 Soltan, M. A., A. Z. Hegazi, S. M. M. El-Laithy, and A. F. Fath El-Bab. 2007. Effect of spawning season, male and female body weight on reproductive performance of Nile tilapia, Oreochromis niloticus. Journal of the Egyptian Veterinary Medical Association 67: 97–108.
13 Fessehaye, Yonas, Zizy El-bialy, Mahmoud A. Rezk, Richard Crooijmans, Henk Bovenhuis, and Hans Komen. 2006. Mating systems and male reproductive success in Nile tilapia (Oreochromis niloticus) in breeding hapas: A microsatellite analysis. Aquaculture 256: 148–158. https://doi.org/10.1016/j.aquaculture.2006.02.024.
14 Fayed, W., A. El-Dahhar, S. El-Zaeem, Z. El-Greisy, M. Salama, and G. Sallam. 2014. Influence of Protein Levels and Pond Fertilization during Broodstock Pre-Spawning Period on the Tolerance of Nile Tilapia, Oreochromis niloticus, Fry to Winter Season Temperature. Mediterranean Aquaculture Journal 6: 1–13. https://doi.org/10.21608/maj.2014.4623.
15 El-Sayed Farag, Mohamed. 2003. Reporoductive performance of Oreochromis niloticus through three seasons in eaarthen ponds. Egyptian Journal of Aquatic Biology and Fisheries 7: 263–282. https://doi.org/10.21608/ejabf.2003.1794.
16 Maia, C.M. 2024. Personal communication.
17 Saboya, J. P. S., G. S. Araujo, J. W. A. Silva, J. Sousa Junior, R. L. Maciel, and W. R. L. Farias. 2012. Efeito dos polissacarídeos sulfatados da rodofícea Kappaphycus alvarezii em pós-larvas de tilápia do Nilo (Oreochromis niloticus) submetidas a situações de estresse. Acta Scientiarum. Animal Sciences 34: 215–221. https://doi.org/10.4025/actascianimsci.v34i3.13213.
18 El-Sayed, A-F M, A El-Ghobashy, and M Al-Amoudi. 1996. Effects of pond depth and water temperature on the growth, mortality and body composition of Nile tilapia, Oreochromis niloticus (L.). Aquaculture Research 27: 681–687. https://doi.org/10.1046/j.1365-2109.1996.00776.x.
19 Gilbert, P. 1996. Breeding and propagation of tilapia (Oreochromis niloticus) in a floating hatchery, Gabon. Naga, the ICLARM Quarterly 19: 26–33.
20 Abaho, Ivan, Thaddeus Zaabwe, Andrew Izaara, Howard N. Kasigwa, Norman Mushabe, Steven Byenkya, Mujibu Nkambo, Sylvester D. Baguma, David L. N. Hafashimana, and Jackson Efitre. 2020. Effect of stocking density on growth and survival of Nile tilapia (Oreochromis niloticus, Linnaeus 1758) under cage culture in Lake Albert, Uganda. International Journal of Fisheries and Aquaculture 12: 26–35. https://doi.org/10.5897/IJFA2018.0671.
21 Romana-Eguia, Maria Rowena R., Ruel V. Eguia, and Rolando V. Pakingking, jr. 2020. Tilapia culture: the basics. Tigbauan, Iloilo, Philippines: Training and Information Division, Southeast Asian Fisheries Development Center Aquaculture Department.
22 Abou, Youssouf, Emile D Fiogbé, and Jean-Claude Micha. 2007. Effects of stocking density on growth, yield and profitability of farming Nile tilapia, Oreochromis niloticus L., fed Azolla diet, in earthen ponds. Aquaculture Research 38: 595–604. https://doi.org/10.1111/j.1365-2109.2007.01700.x.
23 Agyakwah, Seth K., Ruby Asmah, Emmanual T. D. Mensah, Catherine Ragasa, Sena Amewu, Nhuong Tran, Mathew Oyih, and Peter Ziddah. 2020. Farmer’s manual on small-scale tilapia pond farming in Ghana.
24 Xu, Pao, and Junchao Ming. 2018. Status and Trends of the Tilapia Farming Industry Development. In Aquaculture in China: Success stories and modern trends, 404–420. John Wiley & Sons, Ltd.
25 Shoko, Amon Paul, Samwel Mchele Limbu, Hillary Deogratias John Mrosso, Adolf Faustine Mkenda, and Yunus Daud Mgaya. 2016. Effect of stocking density on growth, production and economic benefits of mixed sex Nile tilapia (Oreochromis niloticus) and African sharptooth catfish (Clarias gariepinus) in polyculture and monoculture. Aquaculture Research 47: 36–50. https://doi.org/10.1111/are.12463.
26 Campagnolo, R., A. Freccia, R. R. Bergmann, F. Meurer, and R. A. Bombardelli. 2013. Óleos essenciais na alimentação de alevinos de tilápia do Nilo. Revista Brasileira de Saúde e Produção Animal 14: 565–573.
27 Araujo, G. S., J. A. G. Rodrigues, J. W. A. Silva, and W. R. L. Farias. 2010. Cultivo da tilápia do Nilo em tanques-rede circulares em diferentes densidades de estocagem. Bioscience Journal 26: 428–434. Brazil; Contemporany.
28 Garcia, Fabiana, Daiane M. Romera, Kátia S. Gozi, Eduardo M. Onaka, Fernando S. Fonseca, Sérgio H. C. Schalch, Pedro G. Candeira, et al. 2013. Stocking density of Nile tilapia in cages placed in a hydroelectric reservoir. Aquaculture 410–411: 51–56. https://doi.org/10.1016/j.aquaculture.2013.06.010.
29 Khairnar, Sachin Onkar, A. H. Shanthanagouda, and S. Vijay Kumar Reddy. 2020. Influence of stocking density on growth and physiological responses of Nile tilapia (GIFT strain) in cages. J. Exp. Zool. India 23: 731–735.
30 Costa, Â. A. P., R. Roubach, B. S. L. Dallago, G. W. Bueno, C. McManus, and F. E. M. Bernal. 2017. Influence of stocking density on growth performance and welfare of juvenile tilapia (Oreochromis niloticus) in cages. Arquivo Brasileiro de Medicina Veterinária e Zootecnia 69: 243–251. https://doi.org/10.1590/1678-4162-8939.
31 Siddiqui, A. Q., M. S. Howlader, and A. B. Adam. 1989. Culture of Nile tilapia, Oreochromis niloticus (L.), at three stocking densities in outdoor concrete tanks using drainage water. Aquaculture Research 20: 49–58. https://doi.org/10.1111/j.1365-2109.1989.tb00440.x.
32 Rakocy, J.E. 2005. Cultured Aquatic Species Information Programme. Oreochromis niloticus. Rome: FAO Fisheries and Aquaculture Department.
33 Wang, Kui, Kang Li, Liping Liu, Cristina Tanase, Rainier Mols, and Michiel van der Meer. 2023. Effects of light intensity and photoperiod on the growth and stress response of juvenile Nile tilapia (Oreochromis niloticus) in a recirculating aquaculture system. Aquaculture and Fisheries 8: 85–90. https://doi.org/10.1016/j.aaf.2020.03.001.
34 Brito, L. O., B. R. Simão, J. B. Pereira Neto, G. Cemirames, and C. M. S. B. de Azevedo. 2017. Densidade plantonica do policultivo de Litopenaeus vannamei. Ciência Animal Brasileira 18: e-16840.
35 McDonald, Jennifer L., Mark S. Peterson, and William T. Slack. 2007. Morphology, Density, and Spatial Patterning of Reproductive Bowers in an Established Alien Population of Nile Tilapia, Oreochromis niloticus. Journal of Freshwater Ecology 22: 461–468. https://doi.org/10.1080/02705060.2007.9664176.
36 Bandara, K.V. Sandun N., and Upali S. Amarasinghe. 2017. Factors Related to Nesting Sites of Oreochromis niloticus (Linnaeus 1758; Cichlidae) in Irrigation Reservoirs, Sri Lanka. Asian Fisheries Science 30: 319–335. https://doi.org/10.33997/j.afs.2017.30.4.008.
37 Turner, G. F., and R. L. Robinson. 2000. Reproductive biology, mating systems and parental care. In Tilapias: Biology and Exploitation, ed. Malcolm C. M. Beveridge and Brendan J. McAndrew, 33–58. Dordrecht: Springer Netherlands.
38 El-Ebiary, El Sayed H., Nabil M. Eweedah, El Sayed M. Abdel-Raouf, Ragab M. Abdel-Regal, and Basem S. Abdel-Aty. 2013. Comparative Study between the Performances of Nile Tilapia Oreochromisniloticus during and Out of the Normal Spawning Season. ANGLISTICUM. Journal of the Association-Institute for English Language and American Studies 3.
39 Bautista, A. M., M. H. Carlos, and A. I. San Antonio. 1988. Hatchery production of Oreochromis niloticus L. at different sex ratios and stocking densities. Aquaculture 73: 85–89. https://doi.org/10.1016/0044-8486(88)90043-9.
40 Vera Cruz, Emmanuel M., Eddie Boy T. Jimenez, and Zaldy P. Bartolome. 2023. Shading Influenced Water Quality and Seed Production of Nile Tilapia (Oreochromis niloticus L.) in the Hapa-within-Pond System During Warm Months. The Philippine Journal of Fisheries 30: 155–161. https://doi.org/10.31398/tpjf/30.2.2022-0026.
41 Pawson, M.G., and G.D. Pickett. 1996. The Annual Pattern of Condition and Maturity in Bass, Dicentrarchus Labrax, in Waters Around England and Wales. Journal of the Marine Biological Association of the United Kingdom 76: 107. https://doi.org/10.1017/S0025315400029040.
42 Balirwa, J. S. 1990. The present status of the fishery for tilapia in Lake Victoria (Uganda). In , 61–64.
43 Njiru, M., J. E. Ojuok, J. B. Okeyo-Owuor, M. Muchiri, M. J. Ntiba, and I. G. Cowx. 2006. Some biological aspects and life history strategies of Nile tilapia Oreochromis niloticus (L.) in Lake Victoria, Kenya: Biology of Nile tilapia in Lake Victoria. African Journal of Ecology 44: 30–37. https://doi.org/10.1111/j.1365-2028.2006.00610.x.
44 Goudswaard, K., J.H. Wanink, F. Witte, E.F.B. Katunzi, M.R. Berger, and D.J. Postma. 2004. Diel vertical migration of major fish-species in Lake Victoria, East Africa. Hydrobiologia 513: 141–152. https://doi.org/10.1023/B:hydr.0000018179.80116.93.
45 Bwanika, G. N., B. Makanga, Y. Kizito, L. J. Chapman, and J. Balirwa. 2004. Observations on the biology of Nile tilapia, Oreochromis niloticus L., in two Ugandan crater lakes. African Journal of Ecology 42: 93–101. https://doi.org/10.1111/j.1365-2028.2004.00468.x.
46 van Oijen, M. J. P. 1995. Appendix I. Key to Lake Victoria fishes other than haplochromine cichlids. In Fish Stocks and Fisheries of Lake Victoria: A Handbook for Field Observations, ed. Frans Witte and Wim L. T. van Densen, 209–300. Dyfed, Great Britain: Samara Publishing Limited.
47 Froese, R., and D. Pauly. 2014. FishBase. World Wide Web electronic publication. www.fishbase.org.
48 Bwanika, G. N., L. J. Chapman, Y. Kizito, and J. Balirwa. 2006. Cascading effects of introduced Nile perch (Lates niloticus) on the foraging ecology of Nile tilapia (Oreochromis niloticus). Ecology of Freshwater Fish 15: 470–481. https://doi.org/10.1111/j.1600-0633.2006.00185.x.
49 Oso, J. A., I. A. Ayodele, and O. Fagbuaro. 2006. Food and Feeding Habits of Oreochromis niloticus (L.) and Sarotherodon galilaeus (L.) in a Tropical Reservoir. World Journal of Zoology 1: 118–121.
50 Peterson, Mark S., William T. Slack, Gretchen L. Waggy, Jeremy Finley, Christa M. Woodley, and Melissa L. Partyka. 2006. Foraging in Non-Native Environments: Comparison of Nile Tilapia and Three Co-Occurring Native Centrarchids in Invaded Coastal Mississippi Watersheds. Environmental Biology of Fishes 76: 283–301. https://doi.org/10.1007/s10641-006-9033-4.
51 Uddin, M. S., A. Farzana, M. K. Fatema, M. E. Azim, M. A. Wahab, and M. C. J. Verdegem. 2007. Technical evaluation of tilapia (Oreochromis niloticus) monoculture and tilapia–prawn (Macrobrachium rosenbergii) polyculture in earthen ponds with or without substrates for periphyton development. Aquaculture 269: 232–240. https://doi.org/10.1016/j.aquaculture.2007.05.038.
52 Melo, Luis Henrique, Yuri Simões Martins, Rafael Magno Costa Melo, Paula Suzanna Prado, Ronald Kennedy Luz, Nilo Bazzoli, and Elizete Rizzo. 2019. Low salinity negatively affects early larval development of Nile tilapia, Oreochromis niloticus: insights from skeletal muscle and molecular biomarkers. Zygote 27: 375–381. https://doi.org/10.1017/S0967199419000431.
53 Lung’ayia, H. B. O. 1994. Some aspects of the reproductive biology of the Nile tilapia Oreochromis niloticus (L) in the Nyanza Gulf of Lake Victoria, Kenya. In Proceedings of the Second EEC Regional Seminar on Recent Trends of Research on Lake Victoria Fisheries, ed. E. Okemwa, E. O. Wakwabi, and A. Getabu, 121–127. Nairobi: ICIPE SCIENCE.
54 Souza, U. N., V. O. Felizardo, R. T. F. Freitas, C. C. V. Melo, M. R. Ferreira, and R. V. Reis-Neto. 2016. Influência do horário de aplicação e da variedade genética em fêmeas de tilápias Oreochromis niloticus submetidas à indução hormonal com hCG. Arquivo Brasileiro de Medicina Veterinária e Zootecnia 68: 215–223. https://doi.org/10.1590/1678-4162-7716.
55 Heinrich, Wolfgang. 1967. Untersuchungen zum Sexualverhalten in der Gattung Tilapia (Cichlidae, Teleostei) und bei Artbastarden. Advances in Ethology 6: 684–754.
56 Uchida, Hiroshi, Satoshi Ogawa, Mina Harada, Masato Matushita, Munehico Iwata, Yasuo Sakuma, and Ishwar S. Parhar. 2005. The olfactory organ modulates gonadotropin-releasing hormone types and nest-building behavior in the tilapia Oreochromis niloticus. Journal of Neurobiology 65: 1–11. https://doi.org/10.1002/neu.20156.
57 Castro, A. L. S., E. Gonçalves-de-Freitas, G. L. Volpato, and C. Oliveira. 2009. Visual communication stimulates reproduction in Nile tilapia, Oreochromis niloticus (L.). Brazilian Journal of Medical and Biological Research 42: 368–374. https://doi.org/10.1590/S0100-879X2009000400009.
58 Rana, Kausik J. 1986. Parental influences on egg quality, fry production and fry performance in Oreochromis niloticus (Linnaeus) and O. mossambicus (Peters). Doctoral dissertation, U.K.: University of Stirling.
59 Volpato, G. L., C. R. A. Duarte, and A. C. Luchiari. 2004. Environmental color affects Nile tilapia reproduction. Brazilian Journal of Medical and Biological Research 37: 479–483. https://doi.org/10.1590/S0100-879X2004000400004.
60 Fernandes, AFA, ÉR Alvarenga, DAA Oliveira, CG Aleixo, Sa Prado, RK Luz, NLAF Sarmento, EA Teixeira, MR Luz, and EM Turra. 2013. Production of Oocytes of Nile Tilapia (Oreochromis niloticus) for In Vitro Fertilization via Hormonal Treatments. Reproduction in Domestic Animals 48: 1049–1055. https://doi.org/10.1111/rda.12212.
61 Shokr, El-Sayed A. M. S. 2015. Effect of Follicular Stimulating Hormone and Leutinizing Hormone on Reproduction, Physiological and Biochemical Changes of Oreochromis niloticus. Egyptian Academic Journal of Biological Sciences. C, Physiology and Molecular Biology 7: 61–73. https://doi.org/10.21608/eajbsc.2015.13703.
62 Piamsomboon, Patharapol, Nicole Sirisopit Mehl, Sudson Sirivaidyapong, and Janenuj Wongtavatchai. 2019. Assisted reproduction in Nile tilapia Oreochromis niloticus: Milt preservation, spawning induction and artificial fertilization. Aquaculture 507: 139–143. https://doi.org/10.1016/j.aquaculture.2019.04.019.
63 Rana, Krishen. 1988. Reproductive Biology and the Hatchery Rearing of Tilapia Eggs and Fry. In Recent Advances in Aquaculture, ed. James F. Muir and Ronald J. Roberts, 343–406. Dordrecht: Springer Netherlands.
64 Vera Cruz, E. M., and G. C. Mair. 1994. Conditions for effective androgen sex reversal in Oreochromis niloticus (L.). Aquaculture 122: 237–248. https://doi.org/10.1016/0044-8486(94)90513-4.
65 Lima, E. C. R., R. L. Souza, X. F. Wambach, U. L. Silva, and E. S. Correia. 2015. Cultivo da tilápia do Nilo Oreochromis niloticus em sistema de bioflocos com diferentes densidades de estocagem. Revista Brasileira de Saúde e Produção Animal 16: 948–957. https://doi.org/10.1590/S1519-99402015000400018.
66 Carvalho, E. D., A. L. S. Camargo, and A. S. Zanatta. 2010. Desempenho produtivo da tilápia do nilo em tanques-rede numa represa pública: modelo empírico de classificação. Ciência Rural 40: 1616–1622. https://doi.org/10.1590/S0103-84782010000700021.
67 Zhao, Jian, Zhaobin Gu, Mingming Shi, Huanda Lu, Jianping Li, Mingwei Shen, Zhangying Ye, and Songming Zhu. 2016. Spatial behavioral characteristics and statistics-based kinetic energy modeling in special behaviors detection of a shoal of fish in a recirculating aquaculture system. Computers and Electronics in Agriculture 127: 271–280. https://doi.org/10.1016/j.compag.2016.06.025.
68 Faller, U., and L. Debacker. 1988. Density-dependent behavioral shift in Oreochromis niloticus. In ICLARM Conference Proceedings (Philippines). ICLARM.
69 Barcellos, Leonardo José Gil, S. Nicolaiewsky, S M G. De Souza, and F. Lulhier. 1999. The effects of stocking density and social interaction on acute stress response in Nile tilapia Oreochromis niloticus (L.) fingerlings. Aquaculture Research 30: 887–892. https://doi.org/10.1046/j.1365-2109.1999.00419.x.
70 Delcourt, Johann, Christophe Becco, Nicolas Vandewalle, and Pascal Poncin. 2009. A video multitracking system for quantification of individual behavior in a large fish shoal: Advantages and limits. Behavior Research Methods 41: 228–235. https://doi.org/10.3758/BRM.41.1.228.
71 El-Hawarry, Waleed N., Radi A. Mohamed, and Safinaz A. Ibrahim. 2018. Collaborating effects of rearing density and oregano oil supplementation on growth, behavioral and stress response of Nile tilapia (Oreochromis niloticus). Egyptian Journal of Aquatic Research 44: 173–178. https://doi.org/10.1016/j.ejar.2018.06.008.
72 Gauy, Ana Carolina dos Santos, Marcela Cesar Bolognesi, and Eliane Gonçalves-de-Freitas. 2023. Body Tactile Stimulation Reduces the Effects of High Stocking Density on the Welfare of Nile Tilapia (Oreochromis niloticus). Fishes 8: 320. https://doi.org/10.3390/fishes8060320.
73 Saraiva, João L. 2017. Personal communication.
74 Barbosa, J. M., S. S. S. Brugiolo, J. Carolsfeld, and S. S. Leitão. 2006. Heterogeneous growth fingerlings of the Nile tilapia Oreochromis niloticus: effects of density and initial size variability. Brazilian Journal of Biology 66: 537–541. https://doi.org/10.1590/S1519-69842006000300020.
75 Evans, Joyce J., David J. Pasnik, Patrick Horley, Kimberly Kraeer, and Phillip H. Klesius. 2008. Aggression and Mortality among Nile Tilapia (Oreochromis niloticus) Maintained in the Laboratory at Different Densities. Research Journal of Animal Sciences 2: 57–64.
76 Barreto, Rodrigo Egydio, Graziele G. Arantes Carvalho, and Gilson Luiz Volpato. 2011. The aggressive behavior of Nile tilapia introduced into novel environments with variation in enrichment. Zoology 114: 53–57. https://doi.org/10.1016/j.zool.2010.09.001.
77 Pinho-Neto, Candido Ferreira, Caio Akira Miyai, Fabio Henrique Carretero Sanches, Percilia Cardoso Giaquinto, Helton Carlos Delicio, Leonardo José Gil Barcellos, Gilson Luiz Volpato, and Rodrigo Egydio Barreto. 2014. Does sex influence intraspecific aggression and dominance in Nile tilapia juveniles? Behavioural Processes 105: 15–18. https://doi.org/10.1016/j.beproc.2014.02.003.
78 Vieira, Bruna Renata Meletti, Isabela Inforzato Guermandi, Marina Sanson Bellot, Bruno Camargo-dos-Santos, João Favero-Neto, and Percília Cardoso Giaquinto. 2021. The effects of tryptophan supplementation on stress and aggression in Nile tilapia. Journal of Applied Ichthyology 37: 578–584. https://doi.org/10.1111/jai.14186.
79 Neto, João Favero, and Percilia Cardoso Giaquinto. 2020. Environmental enrichment techniques and tryptophan supplementation used to improve the quality of life and animal welfare of Nile tilapia. Aquaculture Reports 17: 100354. https://doi.org/10.1016/j.aqrep.2020.100354.
80 Gauy, Ana Carolina dos Santos, Marcela Cesar Bolognesi, and Eliane Gonçalves-de-Freitas. 2022. Long-term body tactile stimulation reduces aggression and improves productive performance in Nile tilapia groups. Scientific Reports 12: 20239. https://doi.org/10.1038/s41598-022-24696-3.
81 Volpato, G. L., A. C. Luchiari, C. R. A. Duarte, R. E. Barreto, and G. C. Ramanzini. 2003. Eye color as an indicator of social rank in the fish Nile tilapia. Brazilian Journal of Medical and Biological Research 36: 1659–1663. https://doi.org/10.1590/S0100-879X2003001200007.
82 Corrêa, S. A., M. O. Fernandes, K. K. Iseki, and J. A. Negrão. 2003. Effect of the establishment of dominance relationships on cortisol and other metabolic parameters in Nile tilapia (Oreochromis niloticus). Brazilian Journal of Medical and Biological Research 36: 1725–1731. https://doi.org/10.1590/S0100-879X2003001200015.
83 Barreto, Rodrigo Egydio, and Gilson Luiz Volpato. 2006. Ventilatory frequency of Nile tilapia subjected to different stressors. Journal of Experimental Animal Science 43: 189–196. https://doi.org/10.1016/j.jeas.2006.05.001.
84 Gonçalves-de-Freitas, Eliane, and Aline Chimello Ferreira. 2004. Female social dominance does not establish mating priority in Nile tilapia. Revista de Etologia 6: 33–37.
85 Carvalho, Thaís B., Francine Z. Mendonça, Roselene S. Costa-Ferreira, and Eliane Gonçalves-de-Freitas. 2013. The effect of increased light intensity on the aggressive behavior of the Nile tilapia, Oreochromis niloticus (Teleostei: Cichlidae). Zoologia (Curitiba) 30: 125–129. https://doi.org/10.1590/S1984-46702013000200001.
86 Mendonça, Francine Z., and Eliane Gonçalves-de-Freitas. 2008. Nest deprivation and mating success in Nile tilapia (Teleostei: Cichlidae). Revista Brasileira de Zoologia 25: 413–418. https://doi.org/10.1590/S0101-81752008000300005.
87 Longrie, Nicolas, Sam Van Wassenbergh, Pierre Vandewalle, Quentin Mauguit, and Eric Parmentier. 2009. Potential mechanism of sound production in Oreochromis niloticus (Cichlidae). Journal of Experimental Biology 212: 3395–3402. https://doi.org/10.1242/jeb.032946.
88 Zengeya, Tsungai Alfred, Anthony J. Booth, Armanda D. S. Bastos, and Christian T. Chimimba. 2011. Trophic interrelationships between the exotic Nile tilapia, Oreochromis niloticus and indigenous tilapiine cichlids in a subtropical African river system (Limpopo River, South Africa). Environmental Biology of Fishes 92: 479–489. https://doi.org/10.1007/s10641-011-9865-4.
89 Chapman, Lauren J., Colin A. Chapman, and Mark Chandler. 1996. Wetland ecotones as refugia for endangered fishes. Biological Conservation 78: 263–270. https://doi.org/10.1016/S0006-3207(96)00030-4.
90 Chapman, Lauren J., Colin A. Chapman, Richard Ogutu-Ohwayo, Mark Chandler, Les Kaufman, and Amanda E. Keiter. 1996. Refugia for Endangered Fishes from an Introduced Predator in Lake Nabugabo, Uganda. Conservation Biology 10: 554–561. https://doi.org/10.1046/j.1523-1739.1996.10020554.x.
91 Rosenberger, A. E., and L. J. Chapman. 1999. Hypoxic wetland tributaries as faunal refugia from an introduced predator. Ecology of Freshwater Fish 8: 22–34. https://doi.org/10.1111/j.1600-0633.1999.tb00049.x.
92 Schofield, Pamela J., and Lauren J. Chapman. 1999. Interactions Between Nile Perch, Lates niloticus, and Other Fishes in Lake Nabugabo, Uganda. Environmental Biology of Fishes 55: 343–358. https://doi.org/10.1023/A:1007544017989.
93 Tatemoto, P., G. Valença-Silva, Mariana R. Queiroz, and Donald M. Broom. 2021. Living with low environmental complexity increases fear indicators in Nile tilapia. Animal Behaviour 174: 169–174. https://doi.org/10.1016/j.anbehav.2021.02.006.
94 Saraiva, J. L., Margarida Nogueirinha, Rita Teodósio, Cláudia Aragão, Sofia Engrola, and Pablo Arechavala-Lopez. 2021. The effect of tank cover on welfare of farmed Nile tilapia. Applied Animal Behaviour Science: 105396. https://doi.org/10.1016/j.applanim.2021.105396.
95 Delicio, Helton Carlos, Rodrigo Egydio Barreto, Edvaldo Bento Normandes, Ana Carolina Luchiari, and Ana Lúcia Marcondes. 2006. A place preference test in the fish Nile tilapia. Journal of Experimental Animal Science 43: 141–148. https://doi.org/10.1016/j.jeas.2006.01.001.
96 Duponchelle, Fabrice, and Marc Legendre. 2001. Rapid phenotypic changes of reproductive traits in response to experimental modifications of spatial structure in Nile tilapia, Oreochromis niloticus. Aquatic Living Resources 14: 145–152. https://doi.org/10.1016/S0990-7440(01)01109-3.
97 Mendonça, F. Z., G. L. Volpato, R. S. Costa-Ferreira, and E. Gonçalves-de-Freitas. 2010. Substratum choice for nesting in male Nile tilapia Oreochromis niloticus. Journal of Fish Biology 77: 1439–1445. https://doi.org/10.1111/j.1095-8649.2010.02754.x.
98 Obirikorang, Kwasi Adu, Esther Adu Yeboah, Benjamin Apraku Gyampoh, and Seyram Kwadzo Amanie-Adjei. 2022. Effect of road conditions on physiological stress responses and post-transportation growth and survival of Nile tilapia (Oreochromis niloticus) fingerlings. Journal of Applied Aquaculture 34: 180–196. https://doi.org/10.1080/10454438.2020.1825269.
99 Moreira, A. G. L., A. A. C. Coelho, L. F. G. Albuquerque, R. T. Moreira, and W. R. L. Farias. 2015. Efeito do eugenol como agente mitigador do estresse no transporte de juvenis de tilápia do Nilo. Pesquisa Veterinária Brasileira 35: 893–898. https://doi.org/10.1590/S0100-736X2015001100004.
100 Barcellos, Leonardo José Gil, Gilson Luiz Volpato, Rodrigo Egydio Barreto, Ivanir Coldebella, and Daiane Ferreira. 2011. Chemical communication of handling stress in fish. Physiology & Behavior 103: 372–375. https://doi.org/10.1016/j.physbeh.2011.03.009.
101 Deriggi, Graziele Fernanda, Luis Antonio Kioshi Aoki Inoue, and Moraes Gilberto. 2006. Stress responses to handling in Nile tilapia (Oreochromis niloticus Linnaeus): assessment of eugenol as an alternative anesthetic = Respostas metabólicas da tilápia do Nilo (Oreochromis niloticus) submetida ao manuseio e ao anestésico eugenol. ResearchGate 28.
102 Simões, L. N., A. T. M. Gomide, V. M. F. Almeida-Val, A. L. Val, and L. C. Gomes. 2012. O uso do óleo de cravo como anestésico em juvenis avançados de tilápia do Nilo (Oreochromis niloticus). Acta Scientiarum. Animal Sciences 34: 175–181. https://doi.org/10.4025/actascianimsci.v34i2.13022.
103 Mustapha, Moshood Keke, Olatoyosi Taofeek Oladokun, Mubarak Mayowa Salman, Idris Adewale Adeniyi, and Dele Ojo. 2014. Does light duration (photoperiod) have an effect on the mortality and welfare of cultured Oreochromis niloticus and Clarias gariepinus? Turkish Journal of Zoology 38: 466–470.
104 Maia, Caroline Marques, and Gilson Luiz Volpato. 2013. Environmental light color affects the stress response of Nile tilapia. Zoology 116: 64–66. https://doi.org/10.1016/j.zool.2012.08.001.
105 Martins, Catarina I. M., Patricia I. M. Silva, Luis E. C. Conceição, Benjamin Costas, Erik Höglund, Øyvind Øverli, and Johan W. Schrama. 2011. Linking fearfulness and coping styles in fish. PLOS ONE 6: e28084. https://doi.org/10.1371/journal.pone.0028084.
106 Martins, Maurício Laterça, Daniela Takahashi Nomura, Danilo Makoto Yamaguchi Myiazaki, Fabiana Pilarsky, Karina Ribeiro, Marcello Pardi De Castro, and Cristiane Fátima Meldau De Campos. 2004. Physiological and haematological response of Oreochromis niloticus (Osteichthyes: Cichlidae) exposed to single and consecutive stress of capture. Acta Scientiarum. Animal Sciences 26: 449–456. https://doi.org/10.4025/actascianimsci.v26i4.1719.
107 Barreto, Rodrigo Egydio, and Gilson Luiz Volpato. 2007. Evaluating feeding as unconditioned stimulus for conditioning of an endocrine effect in Nile tilapia. Physiology & Behavior 92: 867–872. https://doi.org/10.1016/j.physbeh.2007.06.013.
108 Luchiari, A. C., and F. a. M. Freire. 2009. Effects of environmental colour on growth of Nile tilapia, Oreochromis niloticus (Linnaeus, 1758), maintained individually or in groups. Journal of Applied Ichthyology 25: 162–167. https://doi.org/10.1111/j.1439-0426.2008.01203.x.
109 Barreto, Rodrigo Egydio, and Gilson Luiz Volpato. 2004. Caution for using ventilatory frequency as an indicator of stress in fish. Behavioural Processes 66: 43–51. https://doi.org/10.1016/j.beproc.2004.01.001.
110 Volpato, G. L., and R. E. Barreto. 2001. Environmental blue light prevents stress in the fish Nile tilapia. Brazilian Journal of Medical and Biological Research 34: 1041–1045. https://doi.org/10.1590/S0100-879X2001000800011.
111 Smith, Michael E., Andrew S. Kane, and Arthur N. Popper. 2004. Acoustical stress and hearing sensitivity in fishes: does the linear threshold shift hypothesis hold water? Journal of Experimental Biology 207: 3591–3602. https://doi.org/10.1242/jeb.01188.
112 Roques, Jonathan A. C., Wout Abbink, Femke Geurds, Hans van de Vis, and Gert Flik. 2010. Tailfin clipping, a painful procedure: Studies on Nile tilapia and common carp. Physiology & Behavior 101: 533–540. https://doi.org/10.1016/j.physbeh.2010.08.001.
113 Barreto, Rodrigo Egydio, and Gilson Luiz Volpato. 2006. Stress responses of the fish Nile tilapia subjected to electroshock and social stressors. Brazilian Journal of Medical and Biological Research 39: 1605–1612. https://doi.org/10.1590/S0100-879X2006001200012.
114 Fessehaye, Yonas, Hans Komen, Mahmoud A. Rezk, Johan A.M. van Arendonk, and Henk Bovenhuis. 2007. Effects of inbreeding on survival, body weight and fluctuating asymmetry (FA) in Nile tilapia, Oreochromis niloticus. Aquaculture 264: 27–35. https://doi.org/10.1016/j.aquaculture.2006.12.038.
115 Eissa, A.E., M. Moustafa, I.N. El-Husseiny, S. Saeid, O. Saleh, and T. Borhan. 2009. Identification of some skeletal deformities in freshwater teleosts raised in Egyptian aquaculture. Chemosphere 77: 419–425. https://doi.org/10.1016/j.chemosphere.2009.06.050.
116 Sonu. 2022. Developing high-welfare stunning solutions with Ace Aquatech. Regal Springs.
117 Volstorf, Jenny. 2024. Conclusion.
118 Lambooij, E., M. A. Gerritzen, H. Reimert, D. Burggraaf, and J. W. van de Vis. 2008. A humane protocol for electro-stunning and killing of Nile tilapia in fresh water. Aquaculture 275: 88–95. https://doi.org/10.1016/j.aquaculture.2008.01.026.
119 Oliveira Filho, Paulo Roberto Campagnoli de, Pamela Jenny Montes Girao, Mariza Pires de Melo, and Elisabete Maria Macedo Viegas. 2015. Indicators of stress in tilapia subjected to different stunning methods. Boletim do Instituto de Pesca, São Paulo 41: 335–343.
120 Gonzalez, Daniel Santiago Rucinque. 2021. Unconsciousness assessment through electroencephalography (EEG), in the process of stunning for humane slaughter of Nile tilapia. SÃO PAULO, Brazil: UNIVERSIDADE DE SÃO PAULO FACULDADE DE ZOOTECNIA E ENGENHARIA DE ALIMENTOS.
121 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.
122 Zambrano, Luis, Elsa Valiente, and M. Jake Vander Zanden. 2010. Food web overlap among native axolotl (Ambystoma mexicanum) and two exotic fishes: carp (Cyprinus carpio) and tilapia (Oreochromis niloticus) in Xochimilco, Mexico City. Biological Invasions 12: 3061–3069. https://doi.org/10.1007/s10530-010-9697-8.
123 El-Sayed, A-F M. 1998. Total replacement of fish meal with animal protein sources in Nile tilapia, Oreochromis niloticus (L.), feeds. Aquaculture Research 29: 275–280. https://doi.org/10.1046/j.1365-2109.1998.00199.x.
124 El-Saidy, Deyab M. S. D., and Magdy M. A. Gaber. 2002. Complete Replacement of Fish Meal by Soybean Meal with Dietary L-Lysine Supplementation for Nile Tilapia Oreochromis niloticus (L.) Fingerlings. Journal of the World Aquaculture Society 33: 297–306. https://doi.org/10.1111/j.1749-7345.2002.tb00506.x.
125 Sharda, O. P. Sharma, and V. P. Saini. 2017. Replacement of fishmeal with soybean meal in Nile tilapia (Oreochromis niloticus) Diet. Journal of Entomology and Zoology Studies 5: 845–849.
126 Younis, El-Sayed M., Abdullah S. Al-Quffail, Nasser A. Al-Asgah, Abdel-Wahab A. Abdel-Warith, and Yousef S. Al-Hafedh. 2018. Effect of dietary fish meal replacement by red algae, Gracilaria arcuata, on growth performance and body composition of Nile tilapia Oreochromis niloticus. Saudi Journal of Biological Sciences 25: 198–203. https://doi.org/10.1016/j.sjbs.2017.06.012.
127 Khan, M. S. K., M. A. M. Siddique, and H. Zamal. 2013. Replacement of fish meal by plant protein sources in Nile tilapia (Oreochromis niloticus) diet: growth performance and utilization. Iranian Journal of Fisheries Science 12: 864–872.
128 Abdel-Warith, A.-W., N. Al-Asgah, Y. El-Sayed, A. El-Otaby, and S. Mahboob. 2018. The effect of replacement of fish meal with Amino Acids and Optimized Protein Levels in the diet of the Nile Tilapia Oreochromis niloticus. Brazilian Journal of Biology 79: 703–711. https://doi.org/10.1590/1519-6984.189413.
129 Muin, H., N. M. Taufek, M. S. Kamarudin, and S. A. Razak. 2017. Growth performance, feed Utilization and body composition of nile tilapia, Oreochromis niloticus (Linnaeus, 1758) fed with different levels of black soldier fly, Hermetia illucens (Linnaeus, 1758) maggot meal diet. Iranian Journal of Fisheries Sciences 16: 567–577.
130 El-Ouny, Youssra M., Sahya Maulu, Mohamed A. A. Zaki, Amira A. Helaly, Abdel Aziz M. Nour, Mohammed F. ElBasuini, Eman M. H. Labib, et al. 2023. Effect of fishmeal replacement with dried red wigglers (Eisenia fetida) worm meal on growth and feed utilization, production efficiency, and serum biochemistry in Nile tilapia (Oreochromis niloticus) fingerlings. Aquaculture Reports 29: 101518. https://doi.org/10.1016/j.aqrep.2023.101518.
131 Sarker, Pallab K., Anne R. Kapuscinski, Alison J. Lanois, Erin D. Livesey, Katie P. Bernhard, and Mariah L. Coley. 2016. Towards Sustainable Aquafeeds: Complete Substitution of Fish Oil with Marine Microalga Schizochytrium sp. Improves Growth and Fatty Acid Deposition in Juvenile Nile Tilapia (Oreochromis niloticus). Edited by José L Soengas. PLOS ONE 11: e0156684. https://doi.org/10.1371/journal.pone.0156684.
132 Toyes-Vargas, Eduardo A., Christopher C. Parrish, María Teresa Viana, Laura Carreón-Palau, Paola Magallón-Servín, and Francisco J. Magallón-Barajas. 2020. Replacement of fish oil with camelina (Camelina sativa) oil in diets for juvenile tilapia (var. GIFT Oreochromis niloticus) and its effect on growth, feed utilization and muscle lipid composition. Aquaculture 523: 735177. https://doi.org/10.1016/j.aquaculture.2020.735177.
133 Ayisi, Christian Larbi, Jinliang Zhao, and Jun-Wei Wu. 2018. Replacement of fish oil with palm oil: Effects on growth performance, innate immune response, antioxidant capacity and disease resistance in Nile tilapia (Oreochromis niloticus). PLOS ONE 13: e0196100. https://doi.org/10.1371/journal.pone.0196100.


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