Effect of different rotifers enrichment formula feed on growth and survival of sea bream larvae ("Sparus aurata")

Isabel Ma ía Fe nández A iles Deg ee in Ma ine Science (ULPGC) isabel. e [email protected] Academic yea 2013/2014 Tu o s: Ca men Ma ía He nández-C uz Lidia Robaina Robaina Final assignmen o he Ma ine Science deg ee E ec o di e en o i e s en ichmen o mula eed on g ow h and su i al o sea b eam la ae (Spa us au a a) Isabel Ma ía Fe nández A iles 2 Index Acknowledgemen s 3 TABLE LIST 4 FIGURE LIST 5 ABBREVIATIONS 6 1. In oduc ion 7 1.1 Global si ua ion o aquacul u e 7 1.2 La icul u e 8 1.3 Objec i es 11 2. Ma e ial and me hods 12 3. Resul s 15 3.1 G ow h 15 3.2 Su i al a e 17 3.3 Biomass 17 3.4 Ac i i y es 18 4. Discussion 19 5. Conclusions 22 6. Re e ences 23 Isabel Ma ía Fe nández A iles 3 Acknowledgmen s Desde es a página quisie a mos a mi ag adecimien o a odas aquellas pe sonas que de una o ma u o a u ie on elación con la elabo ación de es e abajo. En especial: A mi amilia, sob e odo a mis abuelos, po su apoyo incondicional du an e oda la ca e a y la ealización de es e abajo. A la D a. Ca men Ma ía He nández-C uz, po su ines imable paciencia y po ayuda me a es o za me cada día más. A Lidia Robaina po la ayuda b indada, a pesa de que es u iese ocupada, siemp e es u o ahí. A Ángelo San ana, po su ayuda en los momen os más di íciles de es e abajo. Sin él la es adís ica no se ía lo mismo. A odos los écnicos del mesocosmos del Pa que cien í ico Tecnológico de Talia e, po su acep ación como una más du an e los casi es meses que es u e allí. A Desi, po su ines imable ayuda y paciencia a la ho a de lle a a cabo es e expe imen o y po enseña me a con ia más en mí misma y se au osu icien e. A Ma io, po su p edisposición a ayuda me, siemp e con una son isa. A mis amigos y compañe os de clase que han es ado allí pa a da me ánimos en es a úl ima e apa de la ca e a, especialmen e a Y onne, Dani y Jesús. Isabel Ma ía Fe nández A iles 4 TABLE LIST Pages Table I. La ae size, weigh , biomass, su i al a e and ac i i y es along he expe imen . 15 Isabel Ma ía Fe nández A iles 5 FIGURE LIST Pages Figu e 1. De elopmen o global aqua ic p oduc ion (aquacul u e and ishe ies) om 1951 o 2011 7 Figu e 2. A e age size o 11 h DPH sea b eam la ae ed wi h he di e en die s 16 Figu e 3. A e age size o 14 h DPH sea b eam la ae ed wi h he di e en die s 16 Figu e 4. A e age weigh o 11 h DPH sea b eam la ae ed wi h he di e en die s 16 Figu e 5. Su i al a e (%) o sea b eam la ae a he end o he expe imen acco ding o di e en die s. The die s wi h he same le e s a e no signi ican ly di e en (p- alue > 0.05) 17 Figu e 6. Biomass (µg) o sea b eam la ae a he end o he expe imen acco ding o di e en die s 18 Figu e 7. La al su i al a e a e ac i i y es a he end o he expe imen acco ding o di e en die s 18 Isabel Ma ía Fe nández A iles 6 ABBREVIATIONS FAO APROMAR PUFAs EPA DHA UV GIA ANOVA DPH Food and Ag icul u e O ganiza ion o he Uni ed Na ions Asociación Emp esa ial de P oduc o es de Cul i os Ma inos de España Polyunsa u a ed a y acids Eicosapen anoic acid 20:5 (n-3) Docosahexanoic acid 22:6 (n-3) Ul a iole Aquacul u e Resea ch G oup Analysis o a iance Days pos ha ch Isabel Ma ía Fe nández A iles 7 1. In oduc ion 1.1 Global si ua ion o aquacul u e Since he beginning o ci iliza ion, he ex ac ion o ma ine esou ces h ough ishe ies and aquacul u e has been p esen . Some examples o his a e ound in Egyp o China whe e, since ancien imes, ishes ha e been b eeding na u ally. E en now, you can ind people aking ca e o ish in small pounds caused by he o e low o he Nile Ri e in Egyp o in Chinese ice ields, whe e ca ps a e also a med wi h he ha es . (Rueda, 2011) Ac ually, he o igin o he ma ine esou ces ha we use is no only om ishe ies, also aquacul u e plays a c ucial ole. Acco ding o epo s om he FAO in 2012, he inc easing o ishe ies has made ha , abou 30% o he ish s ocks we e ound ully exploi ed. Also, he consump ion pe capi a o sea ood (excluding algae) has inc eased om 9.9 kg in 1960 o 19 kg in 2010. This has a o ed he boos o he aquacul u e in he pas h ee decades, ha ing as a consequence an inc ease o he ish global consump ion wi h 8.8% annual a e. This g ow h also is ela ed wi h an inc ease o i s global ish con ibu ion om 9 - 49% in he las 30 yea s (APROMAR, 2013). Figu e 1. Figu e 1. De elopmen o global aqua ic p oduc ion (aquacul u e and ishe ies) om 1951 o 2011. APROMAR 2013 Cu en ly, conside ing only ish, ainbow ou (Onco hynchus mykiss), A lan ic salmon (Salmo sala ) and sea b eam (Spa us au a a) a e, in ha o de , he ish species widely cul u ed in Eu ope (APROMAR, 2013). Isabel Ma ía Fe nández A iles 8 1.2 La icul u e Sea b eam (Spa us au a a) is one o he mos p oduced ish in Spain (APROMAR 2013). I is mainly due o i s ease o cul i a ion and also by i s high g ow h a e (be ween 1.5 and 2 yea s o each comme cial size). Howe e , and despi e he high game e p oduc ion o his specie du ing he h ee mon hs o b eeding, jus 90% o he eggs a e e ilized and a ound 70% o hese ha ch success ully. Mo eo e , only among 20 - 35% o hese la ae pe cen age su i es (O ega, 2009). Mos o his high mo ali y a e occu s du ing ansi ion among endogenous o exogenous eeding. Acco ding o di e en au ho s (Pascual & Yú e a, 1987; Ri e a & Bo e o, 2009), he mo ali y occu ence is mainly due o la ae mo phological limi a ion, in ol ing mou h size, and also physiological es ic ions as a esul o an incomple e de elopmen o he diges i e sys em. Th ough he yea s, a di ec ela ionship be ween he ype and quali y o ood p o ided and he ex en o la al su i al has been demons a ed (Lazo, 2000; Conceição e al., 2010; Ham e e al., 2013). The simplici y o diges i e ac in ha ched la ae, being li le mo e han a s aigh ube wi hou di e en ia ion and wi h a e y low enzyme ac i i y (Go oni e al., 1986), makes elabo a ed die s ine icien a his s age o de elopmen (Lazo, 2000; Izquie do e al., 2000; Conceição e al., 2010). Some au ho s such as Conceição e al. in 2010, no only poin ou o he diges i e sys em o he la ae as he esponsible o a poo die . They also quali ies hem as isual p eda o s, being he mo emen s o li ing p ey he igge o hei eeding esponse. This p eda o y ins inc in he s ages o la al de elopmen suppo s zooplanck on li ing p eys as he mos app op ia e die o la al eeding. Acco ding o Ce ecedo-Ci e a e al. in 2004, o ensu e he supply o la ae by li ing p ey; hey mus ha e ce ain equi emen s such as: ha ing he igh size o he la ae mou h, a slow mo emen , a high a ailabili y and also, hey ha e o s imula e la ae hun ing ins inc . Besides, he p eys mus each all minimum nu i ional equi emen s and, he e o e, wi h easily diges ion o he la ae. Few species o zooplank on each hese equi emen s; among hem we can ind o i e s (B achionus sp.), b ine sh imp and copepods, being he i s wo species he mos widely cul i a ed o he nu i ion pu pose (Lazo, 2000; Conceição e al., 2010). Isabel Ma ía Fe nández A iles 9 Some easons make o i e s an excellen sou ce o li ing p ey o la ae du ing i s i s weeks o exogenous eeding: hey ha e a small size, be ween 70 - 350 μm, a high g ow h a e, he capabili y o esis high popula ion densi ies and an ele a ed ole ance ange o g owing condi ions and managemen . The o i e s also ha e an ele a ed con en o p o ein, be ween 29 - 63% o i s d y weigh (Jeeja e al., 2011). Ne e heless, only be ween 9 - 28% o i s d y weigh is lipid composi ion, which can a y acco ding he die supplied o he o i e s (Conceição e al., 2010). These lipids a e polyunsa u a ed a y acids (PUFAs), belonging o he g oup o phospholipids, which se e as he main ene gy sou ce o ma ine ish la ae in hei ea ly s ages (Rod iguez e al., 1997; Lazo, 2000; Bell e al., 2003; Ham e e al., 2013.). Among hese a y acids, eicosapen aenoic acid (EPA) 20:5 (n-3) and docosahexaenoic acid (DHA) 22:6 (n-3) plays a e y impo an ole. These PUFAs no only jus p o ide ene gy o la ae; hey a e also essen ial o he cell memb anes in eg i y and unc ions (Sa gen e al., 1997; Ri e a & Bo e o, 2009). Despi e ha , some s udies show he limi ed capaci y o ish la ae o con e EPA in o DHA. Sa gen e al. (1997) ha e demons a ed an impo an de iciency o he enzyme del a-5-desa u ase, esponsible o enlonga ion and desa u a ion o PUFAs. Besides, o i e s a e usually ed wi h bake 's yeas , which gi es hem a de icien composi ion o PUFAs ha will be ansmi ed o he la ae by p ey inges ion. So, o imp o e he up ake o hese a y acids, la ae a e eed wi h PUFAs high en iched o i e s h ough mic oalgae o comme cial p oduc s (Ham e e al., 2008; Conceição e al., 2010). This en ichmen mus ha e a 1:2 a io o EPA:DHA acco ding o Lazo (2000), who p o ed ha , in excess, hese PUFAs gene a e ha m ul e ec s on neu onal and op ical sys em o he la ae. Along wi h a die ich in PUFAs, an app op ia e cul u e medium also p omo es la al su i al. The echnique called "g een wa e ", which is based on he addi ion o mic oalgae di ec ly o la al cul u e anks, has achie ed g ea esul s in e ms o inc eased su i al, g ow h and inges ion a e o la ae (Øie e al., 1997; Rei an e al., 1997). Rocha e al. (2008) also p o ed ha he p esence o mic oalgae in anks inc eases he eeding esponse o la ae o sea b eam signi ican ly. Fu he mo e, he “g een wa e ” echnique con ibu e o p ese e he nu i ional alue o p ey (Mak idis & Isabel Ma ía Fe nández A iles 16 0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0 4.5 5.0 5.5 6.0 Die 1 Die 2 Die 3 Die 4 Die 5 Size (mm) DPH 11 Figu e 2. A e age size o 11 h DPH sea b eam la ae ed wi h he di e en die s. 0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0 4.5 5.0 5.5 6.0 6.5 Die 1 Die 2 Die 3 Die 4 Die 5 Size (mm) DPH 14 Figu e 3. A e age size o 14 h DPH sea b eam la ae ed wi h he di e en die s. 0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 Die 1 Die 2 Die 3 Die 4 Die 5 Weigh (μg) DPH 11 Figu e 4. A e age weigh o 11 h DPH sea b eam la ae ed wi h he di e en die s. . Isabel Ma ía Fe nández A iles 17 3.2 Su i al a e Rega ding su i al a es, he da a ob ained a he end o he expe imen showed signi ican di e ences a e pe o m s a is ical analysis (p- alue = 0.013). These di e ences we e ound be ween die 3 (Isoch ysis sp.), which had he highes su i al a e, and die s 1 (DHA P o ein SELCO) and 4 (Dunaliella sp.), bo h wi h he lowes su i al a e as is shown in igu e 5. Howe e , due o he abno mali y o he die 1 da a, which should ha e been one o he bes su i al a es, i is hough ha i could be a p oblem wi h he p oduc . 0.0 1.0 2.0 3.0 4.0 5.0 6.0 7.0 8.0 Die 1 Die 2 Die 3 Die 4 Die 5 Su i al a e (%) Figu e 5. Su i al a e (%) o sea b eam la ae a he end o he expe imen acco ding o di e en die s. The die s wi h he same le e s a e no signi ican ly di e en (p- alue > 0.05) 3.3 Biomass Once he expe imen ended, all he anks had a a iable numbe o su i al la ae o he coun o he biomass and i s subsequen s a is ical analysis. As we can see in he igu e 6, i s dis ibu ion is simila o he ob ained o su i al a e excep ha , in his case, he di e ences o la ae biomass ound be ween die s we e no signi ican . I was also shown ha he highes biomass was ound in he anks whe e la ae we e ed wi h die 3 (167.57 mg) while he lowes we e again in anks whose la ae we e ed wi h die s 1 (DHA P o ein SELCO) and 4 (Dunaliella sp.), being he las one he die wi h he lowes ob ained biomass (Figu e 6). a a b ab ab Isabel Ma ía Fe nández A iles 18 0 20 40 60 80 100 120 140 160 180 Die 1 Die 2 Die 3 Die 4 Die 5 Biomass (μg) Figu e 6. Biomass (µg) o sea b eam la ae a he end o he expe imen acco ding o di e en die s. 3.4 Ac i i y es Obse ing he esul s o ac i i y es (Figu e 7), a simila dis ibu ion was ound o hose ob ained o su i al and biomass (Figu es 5 and 6 espec i ely). I was mo eo e obse ed ha la ae ed wi h die s 1 and 4 showed a dec easing su i al a e a e he applied s ess, whe eas la ae ed wi h die 3 we e he mos a e mo e esis an , wi h 86.67% o su i al. 0 10 20 30 40 50 60 70 80 90 100 Die 1 Die 2 Die 3 Die 4 Die 5 Su i al a e (%) Figu e 7. La al su i al a e a e ac i i y es a he end o he expe imen acco ding o di e en die s. Isabel Ma ía Fe nández A iles 19 4. Discussion Analyzing he esul s, we can’ see any concluding esponse be ween es ed die s ega ding he size o sea b eam la ae a he samplings o he expe imen . Bu wi h weigh da a ob ained, we can see a sligh end owa d highe weigh in die 5 (bake ’s yeas ). Tha end migh be ela ed wi h low biomass le els ound in he la ae anks ed wi h ha die . This inc ease in la al g ow h associa ed wi h dec eased biomass has also been desc ibed by Roo e al. in 2010. They es ed la al g ow h a di e en densi ies, esul ing in a highe g ow h a e a low densi ies (> 50 la ae L-1). So, hey p o ed ha high la al densi ies a e associa ed wi h low a es o g ow h due o a dec eased appe i e, an inc eased agg essi eness o la ae and he e o e an in ense in aspeci ic compe i ion o ood esou ces. All his igge ed a ch onic s ess si ua ion in la ae, dec easing he biomass o he sys em and a o ing he su i al o la ae be e adap ed and mo e esis an (He nandez-C uz e al., 1999). Howe e , he abo e desc ibed o biomass o die s 1 (DHA P o ein SELCO) and 4 (Dunaliella sp.), whe e he e a e e en less biomass in he anks han in die 5, does no co espond wi h he esul s ob ained o a e age weigh , which alues should be highe . Du ing his wo k, i has been exposed a many imes he g ea impo ance o he in ake o hese a y acids in he la ae. Many au ho s ha e ound in hem he esponse o an inc ease o dec ease o g ow h and su i al in hese ea ly s ages o la al de elopmen (Salhi, 1997; Rod íguez e al., 1994; Salhi e al., 1994). The da a ob ained o die s 1 and 4, does no i wi h he desc ibed by He nández-C uz e al. (1999) and Roo e al. (2010), showing hen a poo ly PUFAs en iched die o la ae. Yeas supplied o o i e s in he die 5, had a ound 1.3% o PUFAs [1] while he die 4, made om he mic oalga Dunaliella sp., has only a ound 0.4 - 0.8% o hese a y acids (Ne ejan e al., 2003). This ag ees wi h he da a obse ed o us. Howe e , he da a ob ained o die 1 do no co espond o expec a ions. A s udy by Sil a in 1999 e alua ed he con en o PUFAs in o i e s en iched wi h DHA P o ein SELCO, ob aining le els o EPA and DHA o 12.1 and 25.2 mg g-1 o d y weigh o EPA and DHA espec i ely. Isabel Ma ía Fe nández A iles 20 These le els canno be compa ed wi h hose ob ained o o i e s en iched wi h yeas which, acco ding o Wa anabe e al. in 1983, anging om 1 o 2 mg g-1 o d y weigh o EPA. This is why i ’s hough ha he anomalous da a ound in he die 1 could be explained as a possible esul o a a y acid oxida ion, pe haps due o a poo main enance o he p oduc . This would be cla i ied in pa analyzing he biochemical composi ion o he die s, bu ha is no he objec i e o his expe imen . On he o he hand, we also ha e high le els o PUFAs in die 3, made om Isoch ysis sp., which do no show an inc ease in a e age la al g ow h compa ed wi h he o he die s es ed wi h lowe con en o hese a y acids. Acco ding Hue limann e al. (2010), his mic oalgae has a ound 8.5 - 15.9% o d y weigh o PUFAs. Sil a in 1999 pe o med an expe imen o analyze he le el o PUFAs in Isoch ysis galbana en iched o i e s, ob aining a composi ion be ween 15 - 20 mg g-1 o d y weigh in EPA and DHA. These alues a e e y simila o hose ob ained by his au ho in o i e s en iched wi h DHA P o ein SELCO. Howe e , o he anks ed wi h die 3, high biomass was obse ed, which we e also epo ed by He nandez-C uz e al. (1999), and la e on by Roo e al. (2010). They s a ed ha an inc ease biomass is associa ed wi h educed g ow h o he la ae. Howe e , nei he he su i al a e no he la ae esis ance we e no educed by his high biomass due o he high PUFAs le els in he die . Simila ly wi h he die 3, he die 2 (Te aselmis sp.) exhibi s low alues o a e age weigh and high in e ms o biomass, su i al and esis ance. Howe e , despi e ha ing ela i ely high le els o PUFAs (0.7 - 3.8% o d y weigh o algae acco ding Hue limann e al. in 2010), his die does no exceed he alues achie ed by die 3 in any espec . Se e al au ho s a gue ha his may be due o he high equi emen s o DHA compa ed o EPA in la ae as a esul o he high a e o g ow h and de elopmen o issues and s uc u es in he la al s age (Takeuchi e al., 1994; Ri e a & Bo e o, 2009). DHA has been desc ibed as an impo an componen o he issue neu al la ae and also imp o es ision and, consequen ly, be e ca ch p ey which leads o a be e ed (Rod iguez e al., 1997; Fu ui a e al., 2000; Ri e a & Bo e o, 2009). Tha is he eason why, despi e ha die 3 has a lowe con en o EPA han die 2, possessing a much highe alue o he DHA imp o es la ae de elopmen . Isabel Ma ía Fe nández A iles 21 Finally, la ae ed wi h die s 2 and 3 showed a highe esis ance o s ess caused by he ac i i y es , bu la ae ed wi h die 3 ob ained he bes esul s. An expe imen conduc ed by Takeuchi e al. (1991) wi h la ae o Japanese sea b eam (Pag us majo ), showed ha hose ed la ae wi h a DHA ich die s pe o med be e su i al a e be o e he es ac i i y han whose la ae which we e ed wi h die s ich in EPA. Isabel Ma ía Fe nández A iles 22 5. Conclusions The g ow h o he la ae is highly dependen on he ank la ae densi y, and hus highe in ensi y o la ae compe i ion du ing eeding. A educ ion o numbe o la ae pe ank appea s a possible educ ion o his p oblem. Among he es ed die s, he use o mic oalgae Dunaliella sp. o o i e s en ichmen does no p o ide accep able esul s in la al g ow h and su i al a e. By he o he hand, he mic oalgae Te aselmis sp., and despi e i s high le els o EPA, does no p o ide enough PUFAs o la ae mainly by i s low DHA con en . High DHA con en die s, as ha con aining Isoc hysis sp. in p esen expe imen , p omo e be e su i al and s ess esis ance o he la ae. Isabel Ma ía Fe nández A iles 23 6. Re e ences APROMAR (2013). La acuicul u a en España 2013. APROMAR, ESACUA, Fundación OESA Bell, J. G., McE oy, L. A., Es e ez, A., Shields, R. J., & Sa gen , J. R. (2003). Op imising lipid nu i ion in i s - eeding la ish la ae. Aquacul u e, 227(1), 211-220. Ci e a-Ce ecedo, R., Al a ez-González, C. A., & Moyano-López, F. J. (2004). Nu ición y alimen ación de la as de peces ma inos. A ances en nu ición acuícola VII. Memo ias del VII Simposium In e nacional de nu ición Acuícola, He mosillo, Sono a, México. FAO (2012). El es ado mundial de la pesca y la acuicul u a 2012. Roma. 231 págs. Fu ui a, H., Tanaka, H., Yamamo o, T., Shi aishi, M., & Takeuchi, T. (2000). E ec s o n-3 HUFA le els in b oods ock die on he ep oduc i e pe o mance and egg and la al quali y o he Japanese lounde , Pa alich hys oli aceus. Aquacul u e, 187(3), 387-398. Go oni, J. J., Boehle , G. W., & Wa anabe, Y. (1986). The physiology o diges ion in ish la ae. En i onmen al Biology o Fishes, 16(1-3), 59-77 Ham e, K., S i as a a, A., Rønnes ad, I., Mango ‐Jensen, A., & S oss, J. (2008). Se e al mic onu ien s in he o i e B achionus sp. may no ul il he nu i ional equi emen s o ma ine ish la ae. Aquacul u e Nu i ion, 14(1), 51-60. Ham e, K., Yú e a, M., Rønnes ad, I., Boglione, C., Conceição, L. E., & Izquie do, M. (2013). Fish la al nu i ion and eed o mula ion: knowledge gaps and bo lenecks o ad ances in la al ea ing. Re iews in Aquacul u e, 5(s1), S26- S58. He nández-C uz, C. M., Salhi, M., Bessona , M., Izquie do, M. S., González, M. M., & Fe nández-Palacios, H. (1999). Rea ing echniques o ed po gy (Pag us pag us) du ing la al de elopmen . Aquacul u e, 179(1), 489-497. Hue limann, R., De Nys, R., & Heimann, K. (2010). 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