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Article

Domestication of Marine Fish Species: Update and Perspectives

by
Fabrice Teletchea
Research Unit Animal and Functionalities of Animal Products (URAFPA), University of Lorraine—INRA, 2 Avenue de la Forêt de Haye, BP 172, 54505 Vandoeuvre-lès-Nancy, France
J. Mar. Sci. Eng. 2015, 3(4), 1227-1243; https://doi.org/10.3390/jmse3041227
Submission received: 31 July 2015 / Accepted: 12 October 2015 / Published: 15 October 2015
(This article belongs to the Special Issue Genetic Breeding Technology and Its Application in Marine Aquaculture)

Abstract

:
Domestication is a long and endless process during which animals become, generations after generations, more adapted to both captive conditions and humans. Compared to land animals, domestication of fish species has started recently. This implies that most farmed marine fish species have only changed slightly from their wild counterparts, and production is based partly or completely on wild inputs. In the past decades, global marine fish production has increased tremendously, particularly since the 1990s, to reach more than 2.2 million tons in 2013. Among the 100 marine fish species listed in the FAO’s database in 2013, 35 are no longer produced, and only six have a production higher than 100,000 tons. The top ten farmed marine species accounted for nearly 90% of global production. The future growth and sustainability of mariculture will depend partly on our ability to domesticate (i.e., control the life cycle in captivity) of both currently farmed and new species.

1. Introduction

Domestication is a long and endless process during which animals become, generations after generations, more adapted to both captive conditions and humans [1,2,3]. Therefore, domestication should not be confused with taming, which is conditioned behavioral modification of wild-born animals [3,4]. During domestication, captive animals are progressively modified from their wild ancestors and at a certain moment are considered domesticated. Nevertheless, it is difficult to determine when captive animals have become domesticated, and such a decision is subjective and arbitrary [1]. According to most authors, a domesticated animal is bred in captivity and thereby modified from its wild ancestors in ways making it more useful to humans who control its reproduction and its food supply [4,5,6].
Domestication on land started about 12,000 years ago [4]. Over millennia, animal populations were modified by humans and changes in behavior, physiology and morphology occurred [6,7]. At the beginning of the twentieth century, modern breeding programs were initiated leading to dramatic changes in productivity, e.g., increase laying rate for laying hens or improved feed conservation ratio, meat yield and growth rate in broiler chickens [2,8,9]. As a result, thousands of genetically distinct livestock breeds have been created, and there is an apparent dichotomy between domesticated species and their wild congeners, which have sometimes gone extinct [6,10,11].
Compared to the domestication of land animals, the domestication of aquatic animals is a recent phenomenon [5]. Except for few species, such as the common carp (Cyprinus carpio) and the goldfish (Carassius auratus), the bulk of farming has started in the past century [5,12,13]. Most fish species farmed today are not much different from their wild conspecifics [9,10,13,14,15]. It is estimated that 90% of the global aquaculture industry is based on wild, undomesticated or non-selectively bred stocks [2,16]. Conversely, less than 10% of aquaculture production comes from selectively bred farm stocks [2]. The Atlantic salmon (Salmo salar) is an outlier, as almost 100% of the total production is based on selectively bred stocks [8,16]. Consequently, depending on the species considered, the control over aquaculture production can vary from managing only a portion of the life cycle to managing the complete life cycle in captivity [11,14,17,18,19,20]. In order to better describe the various fish production strategies, Teletchea and Fontaine [20] proposed a new classification based on the level of human control over the life cycle of farmed species and independence from wild inputs. This classification comprises five levels of domestication with one being the least domesticated to five being the most domesticated. Among the 250 species recorded in the Food and Agriculture Organization (FAO) database in 2009, 39 belong to level 1 (first trials of acclimatization to the culture environment), 75 to the level 2 (part of the life cycle closed in captivity, also known as capture-based aquaculture), 61 to the level 3 (entire life cycle closed in captivity with wild inputs), 45 to the level 4 (entire life cycle closed in captivity without wild inputs) and 30 to the level 5 (selective breeding programs are used focusing on specific goals) [20].
The main goal of the present study is to analyze the evolution of the aquaculture production of marine fish species since 1950, while updating the number of species per domestication level since 2009.

2. Materials and Methods

The central source of data about the world’s fisheries and aquaculture operations is the United Nation’s Food and Agriculture Organization (FAO). With fisheries catch and aquaculture production data going back to 1950, the FAO’s database is an invaluable source of temporal information about the quantity, value, and geographic location of global seafood production [19]. Nevertheless, concerns have been raised in the past two decades about the quality of the data, mainly due a lack of clarity and transparency in terms of what is and is not being reported as “aquaculture”, if reported at all [19,21]. However, a full discussion of these concerns lay outside the scope of this paper (instead, see [19,22]). In the present study, I choose to focus on marine fish species, thus excluding diadromous species, such as Atlantic salmon [23]. The domestication level for all marine fish species listed in the FAO in 2013 (n = 100 species) was determined based on [20] for species already in the database in 2009 (n = 87), and on the literature for “new” species (n = 17). Group of species were excluded.

3. Results

3.1. Evolution of Global Marine Fish Aquaculture Production

Global marine fish production increased slightly from 1950 up to the beginning of the 1970s. Then, the production increased steadily up to the 1990s; thereafter, it rose tremendously (Figure 1). However, more than half of the production is not identified at the species level in the FAO database (Figure 1). One group called “Marine fish nei (not elsewhere included)” totaled 621,275 tons, which is more than one-quarter of the global production in 2013.
Figure 1. Evolution of global aquaculture production of marine fish species. Group of species, not identified at the species level (upper part, in grey), identified at the species level (lower part, in black).
Figure 1. Evolution of global aquaculture production of marine fish species. Group of species, not identified at the species level (upper part, in grey), identified at the species level (lower part, in black).
Jmse 03 01227 g001
In 2013, global marine fish production reached more than 2.2 million tons (Figure 1), which represents about half the production of diadromous fish and about 6% of freshwater fish production (Figure 2). This implies that despite its strong increase, marine fish aquaculture remains small compared to non-marine fish production.
Marine fish are mainly produced in Asia (83.1%), followed by Europe (9.2%) and Africa (7.1%) (Figure 3a). Asia is also the main producer of diadromous fish (39.0%); yet the production is more evenly distributed in the world, with Europe (37.8%) and the Americas (21.9%) (Figure 3b). For freshwater fish, almost the entire production (93.8%) is realized in Asia (Figure 3c).
Figure 2. Comparison of the aquaculture production of marine fish species (black) with those of diadromous (grey) and freshwater (white) species in 2013. The first number is the total production followed by the percentage in parentheses.
Figure 2. Comparison of the aquaculture production of marine fish species (black) with those of diadromous (grey) and freshwater (white) species in 2013. The first number is the total production followed by the percentage in parentheses.
Jmse 03 01227 g002
Figure 3. Main aquaculture regions of fish species in 2013: (a) marine fish species; (b) diadromous fish species; and (c) freshwater fish species.
Figure 3. Main aquaculture regions of fish species in 2013: (a) marine fish species; (b) diadromous fish species; and (c) freshwater fish species.
Jmse 03 01227 g003

3.2. Evolution of the Number of Farmed and Domesticated Fish Species

The number of farmed species has strongly increased in the past decades to reach 65 in 2013 (Figure 4). Since the mid-1990s, the number has doubled, despite slight decreases in 1997, 1998, 2006, 2007, 2009, 2011 and 2012.
Figure 4. Evolution of the number of marine fish species farmed per year.
Figure 4. Evolution of the number of marine fish species farmed per year.
Jmse 03 01227 g004
The comparison between 2009 and 2013 showed that 87 species were listed in 2009 and 100 in 2013. Four species listed in 2009 are no longer present in 2013, the striped weakfish (Cynoscion striatus), the eastern pomfred (Schuettea scalaripinnis), the streamerish (Agrostichthys parkeri) and the rice-paddy eel (Pisodonophis boro). Seventeen “new” species were present (in bold in Appendix). Among the 100 species listed in the FAO database, 35 were no longer produced in 2013, 24 had a production less than 100 tons, 13 had a production between 100 and 1000 tons, 13 species between 1001 and 10,000, nine species between 10,001 and 100,000, and only six have a production higher than 100,000 tons. The domestication level of marine species ranged from one to five (Figure 5). The domestication level for each species is provided in the Appendix. There are only slight differences between 2009 and 2013: only the numbers of species at levels 1, 2 and 3 have increased.
Figure 5. Domestication level of marine fish species in 2009 (grey) and 2013 (black).
Figure 5. Domestication level of marine fish species in 2009 (grey) and 2013 (black).
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The top ten marine farmed species in 2013 totaled 86.5% of the global production, which was 1,241,149 tons (when excluding groups not identified at the species level). These species are almost exclusively produced in Asia, except for the two leading species, gilthead seabream (Sparus aurata) and European sea bass (Dicentrarchus labrax), for which about half of the production is in Europe (Figure 6).
Figure 6. Aquaculture production of the top ten farmed marine species. Gilthead seabream (GS); European seabass (ES); Japanese amberjack (JA); Japanese seabass (JS), subnose pompano (SP); large yellow croaker (LYC); turbot (T); red drum (RD); silver seabream (SS) and cobia (C) (see Appendix for scientific names).
Figure 6. Aquaculture production of the top ten farmed marine species. Gilthead seabream (GS); European seabass (ES); Japanese amberjack (JA); Japanese seabass (JS), subnose pompano (SP); large yellow croaker (LYC); turbot (T); red drum (RD); silver seabream (SS) and cobia (C) (see Appendix for scientific names).
Jmse 03 01227 g006

4. Discussion

4.1. Evolution of Marine Fish Aquaculture Production

Aquaculture, the farming of aquatic organisms, including fish, shellfish and mollusks (excluding plants), is the fastest growing food production system globally, with an increase in production of about 9.3% per year since 1985 [14]. In 2012, aquaculture production has reached 66.7 million tons [2]. Despite a strong increase in the past two decades, the production of marine fish species is still small compared to global aquaculture, and particularly mariculture, which is dominated by mollusks and crustaceans [7]. In comparison, fish is totally dominant in freshwater aquaculture (>99%) [7].
When compared with the two other groups of fish listed in the FAO database, it appears that marine fish species represent a very small amount of global fish production (Figure 2). This is partly due to the fact that farming of most marine fish species is very recent, and thus the life cycle is controlled in captivity for only a handful of species (see below). In addition, several constraints have restricted the expansion of aquaculture of marine fish species, particularly in North America and Europe (Figure 3), among which limited areas sheltered from ocean swells, regulatory restrictions on sites, other competitive factors, such as tourism and port development, the relatively high costs (e.g., investments in infrastructure, maintenance, cost and transport of feed), and the high developmental costs and risks associated with off-shore aquaculture technologies [7,9,24,25,26,27,28].
Today, the marine environment contributes less than two percent of the human food supply [27,29]. It is largely because the development of controlled food production in the ocean lags several millennia behind that on land [12,27,29]. The space used for mariculture production is estimated at about 0.01 million km², or about 0.04% of the global shelf area [29]. Mariculture production is concentrated in a selected number of countries (e.g., China, Spain, Greece, Norway, Chile, and Scotland), particularly in sheltered bays and lagoons [29]. In future decades, it is anticipated that mariculture would increase significantly [9,27,29]. The FAO forecasts that mariculture will reach 54 million metric tons to 70 million metric tons by year 2020 [29]. However, further development of mariculture will run into major bottlenecks concerning the availability, suitability, and cost of feed; space availability; and adverse environmental impacts, which must be overcome if mariculture is to become a major component of global food production [28,29].

4.2. Evolution of the Number of Farmed and Domesticated Marine Species

The number of farmed marine species has strongly increased in the past decades, as observed for other fish groups [5,13,28]. However, only 10 percent of the marine species listed in the FAO in 2013 accounted for nearly 90% of global production (Figure 6). Eight of the top ten farmed species have reached the domestication level 4 (n = 5) or 5 (n = 3). This implies that the entire life cycle of these species has been closed in captivity without the need to use wild inputs, and for three of them, breeding programs have been developed: five for the gilthead seabream (Sparus aurata), three for the European sea bass (Dicentrarchus labrax) and two for the turbot (Psetta maxima) [25]. However, reaching level 4 and 5 does not necessarily imply that the entire aquaculture production of the 19 marine fish species classified at these two domestication levels (Figure 5) is based on domesticated or genetically improved stocks only [11,20]. For instance, even though sea bass has reached the level 5, most farms still rely today on wild broodstock for reproduction or, to lesser extent, from first-generation (F1) individuals and rarely from selected F2 or F3 fish [11].
Achieving full life cycle in captivity over several generations, which could then be called domesticated fish, thus appears an important progress in mastering the sustainability and the increase of production [17]. However, domestication (and notably selection) of a new species is a long and difficult process [30] that requires, among others, broodstock management (production of high quality broodstock, gonad and gamete development, ovulation/oviposition in females and ejaculation of milt in males), incubation of eggs, and rearing of larvae and juveniles [20,25,31]. Therefore, domestication needs access to specific skills, knowledge, and technology, and both long-term public and private funding [2,8,9,13]. This explains why it is has been primarily carried out in developed countries, notably in Europe [25,32].
For all the top ten farmed species, except the large yellow croaker (Larimichthys croceus), the aquaculture production now strongly exceeds capture fisheries (Figure 7). This may be caused by competition between these two sources, because a wild caught fish can commonly be sold at a relatively low price, but cannot be cultured at this low price for a profit. As capture fisheries decline because of overharvesting, the prices of target species often increase dramatically. Under these conditions, aquaculture can thrive, thereby further reducing the value of that capture fishery [14].
Figure 7. Global production of the top ten farmed marine species, aquaculture (black) and fisheries (grey). Gilthead seabream (GS); European seabass (ES); Japanese amberjack (JA); Japanese seabass (JS); subnose pompano (SP); large yellow croaker (LYC); turbot (T); red drum (RD); silver seabream (SS) and cobia (C). The fisheries production of JA, SP and RD are 0, 79, and 204 tons respectively (see Appendix for scientific names).
Figure 7. Global production of the top ten farmed marine species, aquaculture (black) and fisheries (grey). Gilthead seabream (GS); European seabass (ES); Japanese amberjack (JA); Japanese seabass (JS); subnose pompano (SP); large yellow croaker (LYC); turbot (T); red drum (RD); silver seabream (SS) and cobia (C). The fisheries production of JA, SP and RD are 0, 79, and 204 tons respectively (see Appendix for scientific names).
Jmse 03 01227 g007
Two among the top ten farmed species, the Japanese amberjack (Seriola quinqueradiata) and the snubnose pompano (Trachinotus blochii), have only reached level 2, which implies that the entire aquaculture production is based on wild input. This method of production, known as capture-based aquaculture, consists of growing and fattening individuals removed from wild populations [17]. Tuna fattening and much of the marine cage culture in Asia, relies directly on wild-caught small pelagic fish with relatively low market price [19,28,31]. The aquaculture process transforms fish protein from low to high value for human consumption [28]. However, such systems can only function as long as survival and sustainable utilization of the affected wild stocks are warranted [17,19,31]. Therefore, capture-based aquaculture can only be seen as a transitory form of fish production, viable only as long as the wild resource is still available for seed withdrawal [17,31]. Efforts have to be made to domesticate species (i.e., the closing of the life cycle in captivity) to allow a reliable production, independent of wild inputs, and then improve desirable traits through selective breeding [2,25,31].
One-third of the marine species listed in FAO in 2013 are no longer produced, and 50 percent more have a production less than 1000 tons. Nearly all species with a production inferior to 1000 tons have a domestication level between 1 and 3 (Appendix). This highlights that for most species, farming corresponds to one or a few years of aquaculture trial before being abandoned [15,20]. The main reason why numerous attempts with new species fail is that premature attempts to develop industrial enterprises were based on overly optimistic speculation about market demand, rather than on biological and technical knowledge and adequate information about economic feasibility [20,27].

5. Conclusions

Compared to the domestication of land animals, the domestication of aquatic animals, and particularly marine fish species, is a recent phenomenon. Mariculture of fish has only started a few decades ago, and today only a handful of species can be considered domesticated. In contrast, for numerous species, farming was only performed for a few years before being stopped. The future growth and sustainability of mariculture will depend partly on our ability to domesticate (i.e., control the life cycle in captivity) of both currently farmed and new species.

Acknowledgments

The author would like to thank two anonymous reviewers for their comments on a previous draft of the manuscript.

Conflicts of Interest

The author declares no conflict of interest.

Appendix

Table A1. Domestication level for marine fish species listed in the 2013 FAO report (n = 100 species). Group of species were excluded. Species on the list for the first time are in bold (n = 17). Aquaculture production is in tons. When no reliable scientific information was found, species were arbitrarily considered to belong to level 1 when their production was less than five continuous years (n = 15) to the level 2 when their production was between five and up to 10 continuous years (n = 3), and to the level 3 when their production was greater than 10 years (n = 3).
Table A1. Domestication level for marine fish species listed in the 2013 FAO report (n = 100 species). Group of species were excluded. Species on the list for the first time are in bold (n = 17). Aquaculture production is in tons. When no reliable scientific information was found, species were arbitrarily considered to belong to level 1 when their production was less than five continuous years (n = 15) to the level 2 when their production was between five and up to 10 continuous years (n = 3), and to the level 3 when their production was greater than 10 years (n = 3).
Scientific NameCommon NameProduction in 2013Domestication LevelMain Reference
Anarhichas lupusAtlantic wolffish01Gunnarsson et al., 2009, [33]
Atherina boyeriBig-scale sand smelt01Dulcic et al., 2008, [34]
Bolbometopon muricatumGreen humphead parrotfish11
Carangoides malabaricusMalabar trevally3871
Caranx hipposCrevalle jack01
Caranx sexfasciatusBigeye trevally11
Centropristis striataBlack seabass01Rezek et al., 2010, [35]
Chaetodipterus faberAtlantic spadefish01Gaspar 2005, [36]
Dentex tumifronsYellowback seabream01
Dicentrarchus punctatusSpotted seabass21Ly et al., 2012, [37]
Labrus bergyltaBallan wrasse251Muncaster et al., 2010, [38]
Lethrinus miniatusTrumpet emperor451
Lutjanus boharTwo-spotted red snapper01
Megalops atlanticusTarpon01
Micropogonias furnieriWhitemouth croaker51Velloso and Pereira Jr. 2010, [39]
Mugil lizaLebranche mullet71
Muraenesox cinereusDaggertooth pike conger01
Mycteroperca bonaciBlack grouper21
Pagrus majorJapanese seabream01
Platichthys flesusEuropean flounder01Engel-Sørensen et al., 2004, [40]
Pleurogrammus azonusOkhotsk atka mackerel01
Pomatomus saltatrixBluefish01
Scophthalmus rhombusBrill01Cruzado et al., 2004, [41]
Siganus canaliculatusWhite-spotted spinefoot11Xu et al., 2011, [42]
Siganus javusStreaked spinefoot01
Siganus rivulatusMarbled spinefoot01El Dakar et al., 2011, [43]
Valamugil seheliBluespot mullet01Belal 2004, [44]
Acanthopagrus berdaGoldsilk seabream02Liao et al., 2001, [45]
Argyrosomus japonicusJapanese meagre1302Mirimin and Roodt-Wilding, 2015, [46]
Boleophthalmus pectinirostrisGreat blue spotted mudskipper02Zhang et al., 1989, [47]
Centropomus undecimalisCommon snook02Carter et al., 2010a, [48]
Eleutheronema tetradactylumFourfinger threadfin41732Liao et al., 2001, [45]
Epinephelus areolatusAreolate grouper472Ottolenghi et al., 2004, [49]
Epinephelus coioidesOrange-spotted grouper4922Ottolenghi et al. 2004, [49]
Epinephelus fuscoguttatusBrown-marbled grouper862Ottolenghi et al., 2004, [49]
Epinephelus lanceolatusGiant grouper362Peng et al., 2015, [50]
Epinephelus malabaricusMalabar grouper682Ottolenghi et al., 2004, [49]
Gnathanodon speciosusGolden trevally582Liao et al., 2001, [45]
Liza ramadaThinlip grey mullet02Marino et al., 1999, [51]
Lutjanus goldieiPapuan black snapper02
Lutjanus guttatusSpotted rose snapper22García-Ortega 2009, [52]
Lutjanus johniiJohn's snapper2782Liao et al., 2001, [45]
Miichthys miiuyMi-iuy (brown) croaker02An et al., 2012, [53]
Mugil soiuySo-iuy mullet9052
Plectropomus maculatusSpotted coralgrouper72
Polydactylus sexfilisSixfinger threadfin02Deng et al., 2011, [54]
Psammoperca waigiensisWaigieu seaperch5,7042Pham et al., 2010, [55]
Seriola quinqueradiataJapanese amberjack149,7662Bilio 2007b, [56]
Seriola rivolianaLongfin yellowtail4002Roo et al., 2014, [57]
Thunnus albacaresYellowfin tuna1712Wexler et al., 2011, [58]
Thunnus maccoyiiSouthern bluefin tuna3,4822Carter et al., 2010b, [59]
Thunnus thynnusAtlantic bluefin tuna3,4452Carter et al., 2010b, [59]
Trachinotus blochiiSnubnose pompano112,4992Liao et al., 2001, [45]
Trachinotus carolinusFlorida pompano3502Pfeiffer and Riche 2001, [60]
Cromileptes altivelisHumpback grouper23Hong and Zhang 2003, [61]
Dentex dentexCommon dentex543Suquet et al., 2009, [62]
Diplodus sargusWhite seabream243Suquet et al., 2009, [62]
Diplodus vulgarisCommon two-banded seabream03Suquet et al., 2009, [62]
Epinephelus akaaraHong Kong grouper03Hong and Zhang 2003, [61]
Epinephelus tauvinaGreasy grouper5,3543Hong and Zhang 2003, [61]
Evynnis japonicaCrimson seabream03
Liza vaigiensisSquaretail mullet03
Lutjanus argentimaculatusMangrove red snapper5,3573Hong and Zhang 2003, [61]
Lutjanus russelliRussell’s snapper133Hong and Zhang 2003, [61]
Melanogrammus aeglefinusHaddock03Roselund and Skretting 2006, [63]
Pagellus bogaraveoBlackspot seabream 23Suquet et al., 2009, [62]
Pagellus erythrinusCommon pandora03Suquet et al., 2009, [62]
Platax orbicularisOrbicular batfish83Coeurdacier and Gasset 2013, [64]
Pollachius pollachiusPollack03Roselund and Skretting 2006, [63]
Pseudocaranx dentexWhite trevally3,1553
Rhabdosargus sarbaGoldlined seabream33Hong and Zhang 2003, [61]
Sciaena umbraBrown meagre03Bilio 2007a, [65]
Seriola dumeriliGreater amberjack03Hong and Zhang 2003, [61]
Solea senegalensisSenegalense sole6403Imsland 2010, [66]
Solea soleaCommon sole453Imsland 2010, [66]
Sparidentex hastaSobaity seabream5513Teng et al., 1999, [67]
Takifugu obscurusObscure pufferfish4,8603Kim et al., 2010, [68]
Takifugu rubripesTiger pufferfish19,3593Wu et al., 2015, [69]
Thunnus orientalisPacific bluefin tuna16,6243Carter et al., 2010b, [59]
Trachurus japonicasJapanese jack mackerel9583Masuda 2006, [70]
Umbrina cirrosaShi drum1,0703Suquet et al. 2009, [62]
Acanthopagrus latusYellowfin seabream04Hong and Zhang 2003, [61]
Acanthopagrus schlegeliBlackhead seabream1,1614Hong and Zhang 2003, [61]
Anarhichas minorSpotted wolfish04Le François et al. 2010, [71]
Argyrosomus regiusMeagre6,6594Lazo et al., 2010, [72]
Diplodus puntazzoSharpsnout seabream2504Suquet et al., 2009, [62]
Hippoglossus hippoglossusAtlantic halibut1,4854Imsland 2010, [66]
Larimichthys croceusLarge yellow croaker105,2304Bilio 2007b, [56]
Lateolabrax japonicusJapanese seabass129,3344Hong and Zhang 2003, [61]
Mugil cephalusFlathead grey mullet12,2454Hong and Zhang 2003, [61]
Pagrus auratus Silver seabream59,6164Suquet et al., 2009, [62]
Pagrus pagrusRed porgy3504Suquet et al., 2009, [62]
Rachycentron canadumCobia43,3954Bilio 2007a,b, [56,65]
Sciaenops ocellatusRed drum62,1974Lazo et al., 2010, [72]
Sebastes schlegeliKorean rockfish23,7574Bilio 2007b, [56]
Dicentrarchus labraxEuropean seabass161,0595Jobling et al., 2010, [73]
Gadus morhuaAtlantic cod4,2525Björnsson et al., 2010, [74]
Paralichthys olivaceusBastard halibut39,4455Bilio 2007b, [56]
Psetta maximaTurbot76,9985Hulata 2001, [75]
Sparus aurataGilthead seabream173,0625Jobling and Perruzi 2010, [76]

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Teletchea, F. Domestication of Marine Fish Species: Update and Perspectives. J. Mar. Sci. Eng. 2015, 3, 1227-1243. https://doi.org/10.3390/jmse3041227

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Teletchea F. Domestication of Marine Fish Species: Update and Perspectives. Journal of Marine Science and Engineering. 2015; 3(4):1227-1243. https://doi.org/10.3390/jmse3041227

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Teletchea, Fabrice. 2015. "Domestication of Marine Fish Species: Update and Perspectives" Journal of Marine Science and Engineering 3, no. 4: 1227-1243. https://doi.org/10.3390/jmse3041227

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