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Northern pike

Esox lucius

Esox lucius (Northern pike)
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Distribution
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Information


Author: María J. Cabrera-Álvarez
Version: C | 1.1 (2024-12-31)


Reviewer: Jenny Volstorf
Editor: Jenny Volstorf

Initial release: 2023-12-24
Version information:
  • Appearance: C
  • Last minor update: 2024-12-31

Cite as: »Cabrera-Álvarez, María J.. 2024. Esox lucius (WelfareCheck | farm). In: fair-fish database, ed. fair-fish. World Wide Web electronic publication. Version C | 1.1. https://fair-fish-database.net.«





WelfareScore | farm

Esox lucius
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

Esox lucius is a voracious predator that inhabits freshwater streams and lakes of most of the northern hemisphere (i.e., North America, north of Europe, and north of Asia). E. lucius' cannibalistic nature since early stages makes it unsuitable for intensive farming because survival is low even with plenty of food, and the use of live prey (sometimes in polyculture systems) increases production costs. LARVAE and FINGERLINGS are primarily produced for stocking of natural populations, with an optimal harvest size of 7-10 cm (2-5 g) or 4-6 cm to avoid cannibalism. A second use is as predator in polyculture pond systems to suppress commercially less valuable cyprinid species to benefit Cyprinus carpio. Reproduction in captivity is achieved in conditions similar to natural ones as well as with hormonal induction of maturation. Although E. lucius only migrates to spawning grounds, its use of space can be quite large, therefore captive conditions will negatively impact its welfare. Additionally, E. lucius is stressed when in captive conditions and when handled, suffers from malformations both in captivity and in the wild, and there is no stunning and slaughter method implemented specifically for it. All these facts make of E. lucius an undesirable candidate for aquaculture.




1  Home range

Many species traverse in a limited horizontal space (even if just for a certain period of time per year); the home range may be described as a species' understanding of its environment (i.e., its cognitive map) for the most important resources it needs access to.

What is the probability of providing the species' whole home range in captivity?

It is low for minimal farming conditions, as tanks, cages, and some ponds do not cover the whole range in the wild. It is medium for high-standard farming conditions, as other ponds at least overlap with the range in the wild, although we cannot be sure in most age classes. Our conclusion is based on a medium amount of evidence, as wild information in LARVAE, FRY, JUVENILES, and SPAWNERS is missing.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs: does not apply.

LARVAE and FRY:

  • WILD: ponds: 0.1 ha 1, lakes: 130-1,118,000 ha 2, both with unclear home range use.
  • FARM: LARVAE: net cages: 80-100 L 3. FRY: ponds with vegetation 34 <1-3 ha 4; tanks: a few m24; RAS: 1 m35.
  • LAB: does not apply.

JUVENILES:

  • WILD: ponds: 0.1 ha 1 with unclear home range use. Home range of limited extent 67.
  • FARM: ponds with vegetation 34 or conifer branches 4: <1-3 ha 4; earthen ponds: 0.5 ha 5; tanks 3: a few m24.
  • LAB: does not apply.

ADULTS:

  • WILD: undefined home range 89. Extensive movement across 3,500 ha lake, using majority of lake within 49 days 8 or shore of 5,700 ha lake 9. Mostly at 0-500 m of shore 8 or 300 m 9. Close to shore on sunny days and far from shore on windy days, but not deeper 8. No effect of rain on habitat use 8. Daily movements 0-4,000 m, mostly <1,000 m 9, not establishing a territory, but can occupy specific areas for several days or revisit the same areas 679. Ponds: 0.1 ha 1 with unclear home range use.
  • FARM: ponds with vegetation: <1-3 ha 4.
  • LAB: does not apply.

SPAWNERS:

  • WILD: LARVAE and FRY.
  • FARM: ponds with vegetation 3. IND are selected and reared in wintering ponds 3.
  • 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 tanks, RAS, and some ponds do not cover the whole range in the wild. It is medium for high-standard farming conditions, as other ponds at least overlap with the range in the wild. Our conclusion is based on a medium amount of evidence, as further information is needed on farms.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs:

  • WILD: SPAWNERS.
  • FARM: Chase bottles: 5 L, modified Zug bottles: 10 L, for hatching transferred to flat trays 10.
  • LAB: does not apply.

LARVAE and FRY:

  • WILD: ponds: mean 1 m 1. Lakes: in fringe vegetation (F1).
  • FARM: shallow ponds 4; tanks: 0.4-0.5 m 4RAS: 1 m35.
  • LAB: does not apply.

JUVENILES:

  • WILD: ponds: mean 1 m 1, requiring 10 cm depth for every 12 mm of body length or for every week after peak spawning, at least until they reach 150 mm in length 11.
  • FARM: shallow ponds 4: 1.5 m 5; tanks: 0.4-0.5 m 4.
  • LAB: does not apply.

ADULTS:

  • WILD: preference for 0-6 m in lake of 11 m, maybe related to silt substrate in that region 8, 0-4 m 911 but sometimes ≤12 m 11. Ponds: mean 1 m 1.
  • FARM: ponds with vegetation 3.
  • LAB: does not apply.

SPAWNERS:

  • WILD: lakes: range 0.1-0.7 m, mean 0.2-0.4 m 11, 0.2-0.3 m 12, ≤0.5 m, mostly <0.3 m 13, 0.3-1 m 147, 2-3.5 m 12. Ponds: mean 1 m 1.
  • FARM: ponds with vegetation 3.
  • 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 range in captivity overlaps with the migration distance. Our conclusion is based on a medium amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

POTAMODROMOUS15.

Eggs: does not apply.

LARVAE and FRY:

  • WILD: migration in May before noon from spawning grounds to lake motivated by fish size (>20 mm) and natural light 16. Based on distribution (Northern America, north Europe, north Asia), estimated 1-23 h PHOTOPERIOD, freshwater, sometimes brackish water 17.
  • FARM: ponds: 8-16 °C 10. For details of holding systems F2 and F3.
  • LAB: no data found yet.

JUVENILES:

  • WILD: migration in May-June from sloughs to lake 16. Based on distribution (Northern America, north Europe, north Asia), estimated 1-23 h PHOTOPERIOD, freshwater, sometimes brackish water 17.
  • FARM: ponds: 15-20 °C 7. For details of holding systems F2 and F3.
  • LAB: no data found yet.

ADULTS:

  • WILD: no migration outside of spawning season 131819, recaptured IND found not far from spawning ground to <7 km away 12. Movement based on prey availability 19. Based on distribution (Northern America, north Europe, north Asia), estimated 1-23 h PHOTOPERIOD, freshwater, sometimes brackish water 17.
  • FARM: for details of holding systems F2 and F3.
  • LAB: no data found yet.

SPAWNERS:

  • WILD: migration to spawning area within lake or stream 13161915 mostly at night 13. Males arrive earlier than females 1312154, small males earlier than larger males 15. Leave spawning area shortly after spawning 16 (mean 14 days for males, 10 days for females 12), some IND might remain longer periods 16. Return to same spawning grounds 12. Based on distribution (Northern America, north Europe, north Asia), estimated 1-23 h PHOTOPERIOD, freshwater, sometimes brackish water 17.
  • FARM: ponds: 4-10 °C 10. For details of holding systems F2 and F3.
  • 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 (photoperiod and hormonal manipulation, stripping) and may be taken from the wild. It is high for high-standard farming conditions, as natural maturation and natural spawning is possible and 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: does not apply.

JUVENILES: does not apply.

ADULTS: does not apply.

SPAWNERS:

  • WILD: mature December-April 1912 at age 2-3 1219. Spawn annually 12, mostly in March 1319, but also possible in Feb-early May 19 or mid-April 12, then decline in body condition until the end of the summer 19. Spawning from 6:00 to 18:30 13. Male swims closely to or over the female, then pair or group (1-3 males:1 female) reduces speed, male aligns genital opening 13207. Quick recovery after spawning 19. Spawners stay in spawning ground after spawning 16. Sex ratio (male:female): 1:1 (same size) - 3:1 (males smaller size) 13, 2:1 16, 6:1, 7:1, 1:0.1 19.
  • FARM: wild mature IND are caught at their natural spawning ground and stripped 32154. In ponds: breeding only in exceptional circumstances 3. Spontaneous spawning in circumstances close to natural conditions 2223; omitting stripping decreased mortality that would otherwise follow stripping 24. Ponds: males and females are kept together in ponds until show signs of being ready for spawning, then taken out and stripped 10. Reservoirs: temperature and hormonal manipulation to induce maturation and ovulation 2510. Hormonal induction of maturity in males and females followed by stripping 323. Male testes removed (after euthanasia) 10 if insufficient milt is collected by stripping 3 and to prevent contamination of milt with urine or blood 10. Fertilisation solution is needed 3.
  • LAB: no data found yet.



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 and high-standard farming conditions, as – even in the absence of density data in the wild or in farms – we may conclude from the fact that the species is solitary that densities in tanks, RAS, and ponds are potentially stress inducing. Our conclusion is based on a low amount of evidence, as further information is needed for LARVAE, FRY, ADULTS, and SPAWNERS.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs: does not apply.

LARVAE and FRY:

  • WILD: no data found yet.
  • FARM: 100-1,200 IND/L 3. Tanks: 2,000-4,000 IND/m24; RAS: <15 kg/m35. For density and aggression F4.
  • LAB: requires personal space 12. For density and aggression F4.

JUVENILES:

  • WILD: solitary 11. ≤2.7 IND/100 m22, 6.8-13.3 IND/100 m2 262. Poor growth at high densities 2719.
  • FARM: ponds: 22.7 IND/100 m25. For density and aggression F4.
  • LAB: no data found yet.

ADULTS:

  • WILD: solitary 8. Lakes: 9.6-10.5 IND/ha (21.6-23.6 kg/ha) 19, 0.9-200 IND/ha (0.3-115 kg/ha) 7. Poor growth at high densities 2719.
  • FARM: no data found yet.
  • LAB: no data found yet.

SPAWNERS:

  • WILD: spawning in groups, with 1-7 males per female 131619.
  • FARM: ponds: spawning density 2 males:1 female 24.
  • 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 and high-standard farming conditions, as the species is aggressive – even cannibalistic – in almost all age classes and as ways to reduce cannibalism come with caveats: providing live prey is welfare-reducing for the prey species, and decreasing density to a very low level has only been done in restocking. Our conclusion is based on a high amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs: does not apply.

LARVAE and FRY:

  • WILD: cannibalistic 2116, with lower cannibalism when population of insect larvae is high 16.
  • FARM: semi-natural conditions: no cannibalism at densities 6-18 IND/m2 (12-36 IND/m3) at 13-35 mm TOTAL LENGTH, cannibalistic at 18 IND/m2 (36 IND/m3) at 60 mm TOTAL LENGTH28. Size heterogeneity induces cannibalism, even with abundant food available 29. Complexity of habitat does not reduce cannibalism 29. Cannibalistic 21 at 6 IND/m230. 1:10 predator:prey ratio prevents cannibalism 314.
  • LAB: cannibalistic at high densities (unreported number) 12, non-aggressive at low densities (3 IND/18 L) 12.

JUVENILES:

  • WILD: no cannibalism at ≤4.7 IND/100 m2 2. Cannibalism at 6.8-13.3 IND/100 m2 262.
  • FARM: semi-natural conditions: cannibalistic at 6-18 IND/m2 (12-36 IND/m3) at 100 mm TOTAL LENGTH, with increased cannibalism at increasing density 28. High cannibalism 321. Other species used as live prey in polyculture systems with Rutilus rutilus 5324334, Tinca tinca5324334, Lepomis macrochirus5324334 or other cyprinids 5. Ponds: no cannibalism at 9.4 IND/100 m25.
  • LAB: no data found yet.

ADULTS:

  • WILD: no data found yet.
  • FARM: other species used as live prey in polyculture systems with Rutilus rutilus, Tinca tinca, Lepomis macrochirus 324334.
  • LAB: no data found yet.

SPAWNERS:

  • WILD: no territorial behaviour 7, aggressive postures to intruders 7.
  • FARM: no data found yet.
  • LAB: 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, as the species uses substrate, but a) incubation bottles, net cages, tanks, and RAS are devoid of it and b) given stripping in SPAWNERS. It is high for high-standard farming conditions given ponds with vegetation for all age classes (including natural reproduction for SPAWNERS). Our conclusion is based on a high amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs:

  • WILD: scattered on dense vegetation 2071612.
  • FARM: for details of holding systems F3.
  • LAB: no data found yet.

LARVAE and FRY:

  • WILD: in fringe vegetation 191612, dense weedbeds, reed 19.
  • FARM: attachment to tank walls 4. For details of holding systems F2 and F3.
  • LAB: no data found yet.

JUVENILES:

  • WILD: in fringe vegetation, dense weedbeds, reed 19, submerged vegetation with some emergent and floating vegetation 11.
  • FARM: for details of holding systems F2 and F3.
  • LAB: no data found yet.

ADULTS:

  • WILD: silt, sand, rock 8. Unvegetated areas 8 or with aquatic macrophytes (e.g. Scirpus sp.) 8 depending on size (smaller IND more abundant in vegetated areas) 11. Versatile habitat use 811. Avoid turbid waters 8.
  • FARM: for details of holding systems F2 and F3.
  • LAB: no data found yet.

SPAWNERS:

  • WILD: shallow waters 19, marshy areas of lake or connected sloughs 16. Silt and gritty sand 1312. Require vegetation to spawn 131612.
  • FARM: ponds: coarse, stone rip-rap with vegetation 13. For stripping F5.
  • LAB: no data found yet.



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, given we just found data on ADULTS. Our conclusion is based on a low amount of evidence, as further research is needed on all other age classes.

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

JUVENILES:

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

ADULTS:

  • WILD: no data found yet.
  • FARM: stressed by handling 1835, needing ≤2 days to recover 18.
  • LAB: stressed by blood sampling 36, confinement 3738, handling 35 .

SPAWNERS:

  • WILD: no data found yet.
  • FARM: no data found yet.
  • 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 low for minimal farming conditions, as malformation rates may exceed 10%. It is medium for high-standard farming conditions, as some malformations result from conditions that may be changed (storing, incubation temperature, duration in RAS, suspended solids). Our conclusion is based on a medium amount of evidence, as improvement of the situation by adjusting conditions needs more proof.

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: malformations in 0.5% LARVAE independent of egg activation media (tap water, deionized water, water with different NaCl contents) 39.
  • LAB: lower malformation rate (spinal cord torsion, yolk sac, eye deformations, etc.) at 96 h post ovulation (in 15% versus 33%) when eggs were left in female (between ovulation and stripping) than when stored in incubator 40. Malformations in 7% LARVAE when eggs incubated in filtered riverine water, higher frequency of malformations when incubated in unfiltered riverine water (9%) and tap water (10%) probably due to bacteria on suspended solids damaging egg membrane or particles on egg membrane disturbing the oxygen regime inside the egg 41. Malformations in 6.2-10.3% LARVAE when eggs incubated at 6 or 10 °C, higher frequency of malformations when incubated at 14 and 18 °C (12.9-18.2%), highest at 3 °C incubation (76.2%) 42. Malformations in <4% LARVAE and FRY with highest frequency when eggs incubated at 16 °C compared to 8, 10, 12 or 14 °C 43.

JUVENILES:

  • WILD: fins and jaws growth abnormalities (reviewed in 7).
  • FARM: lower malformation rate (11.5% versus 18.4%) of mouth and operculum in IND moved from RAS to ponds at lower size (6.4 cm versus 14.3 cm) indicating a negative effect of longer rearing in RAS5.
  • LAB: no data found yet.

ADULTS:

  • WILD: mutants with accesory fins 4445, pugheadedness (3 in 10,000) 46, snub nose 477, two heads 487, tri-lobed caudal fin 49.
  • FARM: no data found yet.
  • 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 unclear for minimal and high-standard farming conditions, although percussive stunning seems promising, but needs to be verified for the farming context. Our conclusion is based on a low amount of evidence.

Likelihoodscore-li
Potentialscore-po
Certaintyscore-ce

Eggs: does not apply.

LARVAE and FRY: does not apply.

JUVENILES:

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

ADULTS:

  • WILD: does not apply.
  • FARM: no data found yet.
  • LAB: less stressed when stunned by blow to the head than by immersion in anaesthetic (MS-222) 36.

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 450, 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: carnivorous (mostly fish, but also invertebrates) 161930.
  • FARM: preference for live prey over granulated feed 5.
  • LAB: no data found yet.



Side note: Commercial relevance

How much is this species farmed annually?

1,494 t in 2022 51.




Glossary


ADULTS = mature individuals
DOMESTICATION LEVEL 4 = entire life cycle closed in captivity without wild inputs 50
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
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) 34
WILD = setting in the wild



Bibliography


1 Hühn, Daniel, Kay Lübke, Christian Skov, and Robert Arlinghaus. 2014. Natural recruitment, density-dependent juvenile survival, and the potential for additive effects of stock enhancement: an experimental evaluation of stocking northern pike (Esox lucius) fry. Canadian Journal of Fisheries and Aquatic Sciences 71: 1508–1519. https://doi.org/10.1139/cjfas-2013-0636.
2 Sutela, T., P. Korhonen, and K. Nyberg. 2004. Stocking success of newly hatched pike evaluated by radioactive strontium (85Sr) marking. Journal of Fish Biology 64: 653–664. https://doi.org/10.1111/j.1095-8649.2004.00329.x.
3 Horvath, L., G. Tamas, and C. Seagrave. 2002. Carp and Pond Fish Culture: Including Chinese Herbivorous Species, Pike, Tench, Zander, Wels Catfish, Goldfish, African Catfish and Sterlet. 2nd Edition.
4 Kuparinen, Anna, and Hannu Lehtonen. 2018. Northern Pike Commercial Fisheries, Stock Assessment and Aquaculture. In Biology and Ecology of Pike, ed. Christian Skov and P. Anders Nilsson, 1st ed., 123–163. Boca Raton, FL : CRC Press, 2017. | “A Science Publishers book.”: CRC Press. https://doi.org/10.1201/9781315119076-8.
5 Szczepkowski, Mirosław, Zdzisław Zakęś, Andrzej Kapusta, Bożena Szczepkowska, Marek Hopko, Sylwia Jarmołowicz, Agata Kowalska, et al. 2012. Growth and survival in earthen ponds of different sizes of juvenile pike reared in recirculating aquaculture systems. Archives of Polish Fisheries 20. https://doi.org/10.2478/v10086-012-0030-2.
6 Carbine, William F. 1945. Growth potential of the northern pike (Esox lucius). éditeur non identifié.
7 Raat, Alexander J. P. 1988. Synopsis of Biological Data on the Northern Pike: Esox Lucius Linnaeus, 1758. Vol. 2. FAO Fisheries Synopsis 30. Food and Agriculture Organization of the United Nations.
8 Chapman, C. A., and W. C. Mackay. 1984. Versatility in habitat use by a top aquatic predator, Esox lucius L. Journal of Fish Biology 25: 109–115. https://doi.org/10.1111/j.1095-8649.1984.tb04855.x.
9 Diana, James S., W. C. Mackay, and Mark Ehrman. 1977. Movements and Habitat Preference of Northern Pike (Esox lucius) in Lac Ste. Anne, Alberta. Transactions of the American Fisheries Society 106: 560–565. https://doi.org/10.1577/1548-8659(1977)106<560:MAHPON>2.0.CO;2.
10 Bondarenko, V, J Křišťan, V Švinger, and T Policar. 2013. Reproduction and rearing of advanced northern pike (Esox lucius L.) fry. Vodnany 144.
11 Casselman, John M, and Cheryl A Lewis. 1996. Habitat requirements of northern pike 53.
12 Frost, Winifred E., and Charlotte Kipling. 1967. A Study of Reproduction, Early Life, Weight-Length Relationship and Growth of Pike, Esox lucius L., in Windermere. The Journal of Animal Ecology 36: 651. https://doi.org/10.2307/2820.
13 Clark, Clarence F. 1950. Observations on the Spawning Habits of the Northern Pike, Esox lucius, in Northwestern Ohio. Copeia 1950: 285. https://doi.org/10.2307/1437909.
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