黃 迪,任 幸,吳玉波,陳建明,王 巖*
(1.浙江大學(xué)動(dòng)物科學(xué)學(xué)院,杭州310058;2.浙江大學(xué)海洋學(xué)院,浙江舟山316021;3.浙江省淡水水產(chǎn)研究所,浙江魚(yú)類健康與營(yíng)養(yǎng)重點(diǎn)實(shí)驗(yàn)室,浙江湖州310001)
不同投喂-停喂時(shí)間對(duì)大口黑鱸攝食、生長(zhǎng)和廢物排放的影響
黃 迪1,任 幸2,吳玉波1,陳建明3,王 巖2*1
(1.浙江大學(xué)動(dòng)物科學(xué)學(xué)院,杭州310058;2.浙江大學(xué)海洋學(xué)院,浙江舟山316021;3.浙江省淡水水產(chǎn)研究所,浙江魚(yú)類健康與營(yíng)養(yǎng)重點(diǎn)實(shí)驗(yàn)室,浙江湖州310001)
在室內(nèi)循環(huán)水水槽中進(jìn)行8周實(shí)驗(yàn)以評(píng)價(jià)不同投喂-停喂時(shí)間對(duì)初始體質(zhì)量為(14.4±0.3)g的大口黑鱸(Micropterus salmoides)攝食、生長(zhǎng)、食物利用、魚(yú)體組成和氮、磷廢物排放的影響。采用單因素實(shí)驗(yàn)設(shè)計(jì),設(shè)3個(gè)處理:一組正常投喂(S0),另外2組分別投喂3 d停喂1 d(S1)或投喂7 d停喂1 d(S2)。結(jié)果表明:隨投喂-停喂時(shí)間比例的減少,魚(yú)攝食率、體質(zhì)量增加、飼料系數(shù)均呈下降趨勢(shì),但處理組S0、S1和S2之間在氮和磷保留效率、肥滿度、肝體比、全魚(yú)蛋白質(zhì)和脂肪含量、氮和磷廢物排放量方面無(wú)顯著差異;實(shí)驗(yàn)結(jié)束時(shí),S0組最終體質(zhì)量及體質(zhì)量增加均顯著高于S2組(P<0.05),S2組顯著高于S1組(P<0.05),投喂期間S1組和S2組的攝食率和特定生長(zhǎng)率均低于同期S0組,但飼料系數(shù)和氮保留效率與S0組無(wú)顯著差異。此外,S1和S2組在停喂后恢復(fù)投喂期間均表現(xiàn)出部分補(bǔ)償生長(zhǎng),其機(jī)制是增加攝食。根據(jù)本實(shí)驗(yàn)結(jié)果,當(dāng)在大口黑鱸池塘養(yǎng)殖中采用交替投喂和停喂策略時(shí),合理的停喂-投喂時(shí)間應(yīng)分別為13 d和1 d。
補(bǔ)償生長(zhǎng);投喂策略;體質(zhì)量增加;飼料系數(shù);廢物排放
Summary Compensatory growth is described as a phase of accelerated growth when the fish were under favorable circumstances after a period of growth depression,which was widely investigated in the past decades all around the world. Largemouth bass(Micropterus salmoides)is a carnivorous fish species of commercial importance to freshwater aquaculture industry,which is now widely cultured in Guangdong,Zhejiang and Jiangsu provinces.
Researches about nutrition requirements have been established a lot in the past decades,however,quite rarely on compensatory growth and feeding regime of largemouth bass.In order to improve the feeding regime of largemouth bass,the research was conducted.
An 8-week feeding trial was conducted in an indoor re-circulating system to examine the effect of different regimes of feeding and feed deprivation on feed intake,growth,feed utilization,body composition and waste output of juvenile largemouthbass.Three treatments were designed,in which one group was fed with a formulated feed twice daily(S0),one group was fed for 3 days and then deprived offeed for 1 day(S1),and one group was fed for7 days and then deprived offeed for1 day(S2).
The results showed thatthe feed intake,body mass gain and feed conversion ratio(FCR)decreased with the increase ofthe days of feed deprivation.However,no significant difference was found in nitrogen retention efficiency,phosphorus retention efficiency,condition factor,hepatosomatic index,contents of protein and lipid in whole body,and waste outputof nitrogen and phosphorus among the treatments.At the end of the feeding trial,final body mass and mass gain were higher in S0than in S1, while they were higher in S2than in S1.During feeding,both feed intake and specific growth rate were lower in S1and S2than in S0,while no significantdifference was found in nitrogen retention efficency and feed convension ratio between S0and S1or S2.
The above results indicated thatlargemouth bass exhibited partialgrowth compensation when fed with the feeding regimes as S1and S2,and the mechanism of the compensatory growth is attributed to the increased feed intake during re-feeding. According to the results,when using the feeding regime in pond culture of largemouth bass,the optimal ratio between the days for feeding and feed deprivation should be 13d/1d.
魚(yú)類需要從食物中獲取營(yíng)養(yǎng)以滿足生長(zhǎng)和代謝的需求,并可通過(guò)調(diào)整攝食量應(yīng)對(duì)食物豐歉和營(yíng)養(yǎng)組成的變化。確定合理的飼喂策略,包括食物營(yíng)養(yǎng)結(jié)構(gòu)、投喂量和投喂方法,是魚(yú)類養(yǎng)殖技術(shù)體系研究的重要內(nèi)容。有關(guān)魚(yú)類飼料營(yíng)養(yǎng)需求和投喂方法已分別開(kāi)展了大量的研究[1-5],但針對(duì)特定養(yǎng)殖條件下魚(yú)類的飼喂策略的系統(tǒng)研究尚不多見(jiàn)。補(bǔ)償生長(zhǎng)指動(dòng)物在惡劣環(huán)境條件下經(jīng)過(guò)一段時(shí)間的生長(zhǎng)停滯或失重后,當(dāng)環(huán)境條件重新恢復(fù)正常所表現(xiàn)出的超常生長(zhǎng)現(xiàn)象或能力[6-8]。自20世紀(jì)80年代以來(lái),魚(yú)類補(bǔ)償生長(zhǎng)強(qiáng)度以及利用補(bǔ)償生長(zhǎng)原理提高水產(chǎn)養(yǎng)殖魚(yú)類生長(zhǎng)速度和飼料利用效率的方法一度是魚(yú)類生理生態(tài)學(xué)和水產(chǎn)養(yǎng)殖學(xué)研究的熱點(diǎn),但迄今針對(duì)不同魚(yú)類種類和不同環(huán)境限制條件研究得出的結(jié)論存在分歧:部分研究認(rèn)為一些魚(yú)類種類經(jīng)過(guò)營(yíng)養(yǎng)限制后可表現(xiàn)出超補(bǔ)償或完全補(bǔ)償生長(zhǎng)[9];部分研究表明經(jīng)過(guò)營(yíng)養(yǎng)限制魚(yú)類僅能實(shí)現(xiàn)部分補(bǔ)償生長(zhǎng)[10-11]或不表現(xiàn)出補(bǔ)償生長(zhǎng)[12-13]。因此,有關(guān)補(bǔ)償生長(zhǎng)原理在制定魚(yú)類養(yǎng)殖飼喂策略中的作用有待進(jìn)一步探討。
大口黑鱸(Micropterus salmoide s)屬鱸形目、太陽(yáng)魚(yú)科、黑鱸屬,俗稱加州鱸,為淡水肉食性魚(yú)類[1]。大口黑鱸原產(chǎn)地為北美洲,20世紀(jì)80年代引入我國(guó)進(jìn)行人工養(yǎng)殖,目前在廣東、浙江、江蘇等省已形成較大的池塘養(yǎng)殖規(guī)模。有關(guān)大口黑鱸飼料營(yíng)養(yǎng)需求已有較多的研究[1-4],但關(guān)于大口黑鱸補(bǔ)償生長(zhǎng)能力尚未見(jiàn)報(bào)道。本文研究了不同投喂-停喂時(shí)間對(duì)大口黑鱸攝食、生長(zhǎng)、食物利用、魚(yú)體組成和氮、磷廢物排放的影響,目的是確定能否利用補(bǔ)償生長(zhǎng)原理來(lái)改進(jìn)大口黑鱸的投喂技術(shù)。
1.1 實(shí)驗(yàn)魚(yú)和養(yǎng)殖系統(tǒng)
飼養(yǎng)實(shí)驗(yàn)在浙江大學(xué)紫金港校區(qū)水產(chǎn)養(yǎng)殖基地進(jìn)行。所用大口黑鱸魚(yú)種購(gòu)自浙江省德清縣某淡水魚(yú)苗種場(chǎng)。實(shí)驗(yàn)前挑選出270尾大小規(guī)格相近的魚(yú),在9個(gè)室內(nèi)玻璃鋼循環(huán)水水槽(直徑80 cm,高70 cm,容積350 L)內(nèi)馴養(yǎng)2周。馴養(yǎng)密度為30尾/水槽。馴養(yǎng)期間,每天分2次(8:00和16:00)投喂根據(jù)浙江大學(xué)水域生態(tài)系統(tǒng)與水產(chǎn)養(yǎng)殖實(shí)驗(yàn)室配方制作的配合飼料(含粗蛋白質(zhì)50%,粗脂肪9%,灰分13%)[2]。
1.2 實(shí)驗(yàn)設(shè)計(jì)
采用單因素實(shí)驗(yàn)設(shè)計(jì)。設(shè)S0、S1和S23個(gè)處理。S0:每天正常投喂;S1:每投喂3 d停喂1 d;S2:每投喂7 d停喂1 d。實(shí)驗(yàn)時(shí)間為8周;在實(shí)驗(yàn)期間S1組交替投喂-停喂14次,S2組交替投喂-停喂7次。
實(shí)驗(yàn)開(kāi)始前將馴養(yǎng)的魚(yú)停喂24 h,然后集中在一個(gè)水槽中。每次隨機(jī)選取25尾魚(yú),成群稱量后隨機(jī)放入9個(gè)室內(nèi)玻璃鋼循環(huán)水水槽中。實(shí)驗(yàn)魚(yú)初始體質(zhì)量為(14.4±0.3)g。放養(yǎng)后從剩余的暫養(yǎng)魚(yú)中隨機(jī)取3組魚(yú)(每組5尾),分別測(cè)量魚(yú)體質(zhì)量、體長(zhǎng)和肝質(zhì)量,然后保存在冰箱(-20℃)中作為分析魚(yú)體組成的樣品。
實(shí)驗(yàn)期間,每天8:00和16:00按飽食量投喂。每天下午換水1次,換水量約100 L。水槽內(nèi)連續(xù)充氣,并按3 L/min流速與水處理系統(tǒng)循環(huán)。每天下午用虹吸方法將水槽內(nèi)的魚(yú)糞吸出。實(shí)驗(yàn)期間,水溫為(21.1± 1.3)℃,pH為6.8±0.1,溶解氧為(8.6±0.2)mg/L。采用自然光照,光照周期為14 h光照,10 h黑暗。
實(shí)驗(yàn)結(jié)束時(shí),將魚(yú)停喂24 h,然后將每個(gè)水槽內(nèi)的魚(yú)捕出并成群稱量。從每個(gè)水槽內(nèi)隨機(jī)取3尾魚(yú),分別測(cè)量體質(zhì)量、體長(zhǎng)和肝質(zhì)量,然后保存在冰箱(-20℃)中作為分析魚(yú)體組成的樣品。
1.3 化學(xué)分析
將所取的實(shí)驗(yàn)魚(yú)樣品在室溫下化凍、稱量后,放在高壓滅菌鍋內(nèi)(125℃)蒸煮20 min,在105℃下烘干至恒量。將干燥樣品粉碎并通過(guò)40目篩。根據(jù)AOAC方法[14]分析飼料及實(shí)驗(yàn)魚(yú)水分、粗蛋白質(zhì)、脂肪、灰分和磷含量。
1.4 數(shù)據(jù)計(jì)算與統(tǒng)計(jì)分析
攝食率(feed intake,F(xiàn)I)、體質(zhì)量增加(mass gain,MG)、特定生長(zhǎng)率(specific growth rate,SGR)、飼料系數(shù)(feed conversion ratio,F(xiàn)CR)、氮保留效率(nitrogen retention efficiency,NRE)、磷保留效率(phosphorus retention efficiency,PRE)、肥滿度(condition factor,CF)、肝體比(hepatosomatic index,HSI)、飼料氮廢物排放(nitrogen waste output,NWO)和飼料磷廢物排放(phosphorus waste output,PWO)分別按下列公式計(jì)算:
FI/(%/d)=I/[(m0+mt)/2×t]×100;
MG/g=mt/Nt-m0/N0;
SGR/(%/d)=[ln(mt/Nt)-ln(m0/N0)]/t×100;
FCR=I/(mt-m0);
NRE/%=(mt×CNt-m0×CN0+md×CN0)/(I×CNf);

其中:I為實(shí)驗(yàn)期間每個(gè)水槽內(nèi)投喂的飼料量,g;m0和mt分別為實(shí)驗(yàn)開(kāi)始和結(jié)束時(shí)魚(yú)體質(zhì)量,g;N0和Nt為實(shí)驗(yàn)開(kāi)始和結(jié)束時(shí)每個(gè)水槽內(nèi)魚(yú)尾數(shù);t為實(shí)驗(yàn)時(shí)間,d;md為每個(gè)水槽內(nèi)死魚(yú)的總質(zhì)量,g;和分別為實(shí)驗(yàn)開(kāi)始和結(jié)束時(shí)魚(yú)體氮含量,%;和分別為實(shí)驗(yàn)開(kāi)始和結(jié)束時(shí)魚(yú)體磷含量,%;和分別為飼料氮、磷含量,%;ms為實(shí)驗(yàn)開(kāi)始和結(jié)束時(shí)所取樣品魚(yú)的體質(zhì)量,g;Ls為實(shí)驗(yàn)開(kāi)始和結(jié)束時(shí)所取樣魚(yú)的體長(zhǎng),cm;mL為實(shí)驗(yàn)開(kāi)始和結(jié)束時(shí)所取樣品魚(yú)的肝質(zhì)量,g。
采用單因素方差分析檢驗(yàn)不同投喂-停喂時(shí)間對(duì)FI、MG、SGR、FCR、NRE、PRE、CF、HSI、全魚(yú)組成(水分、蛋白質(zhì)、脂肪、灰分和磷)、NWO和PWO的影響。若方差分析差異顯著,用鄧肯檢驗(yàn)進(jìn)一步比較不同處理間的差異。FI、SGR、NRE、PRE、HSI、魚(yú)體組成(水分、蛋白質(zhì)、脂肪、灰分和磷)等用百分?jǐn)?shù)表示的數(shù)據(jù)進(jìn)行方差分析前先經(jīng)過(guò)反正弦變換。取P<0.05為差異顯著性水平。

表1 不同投喂-停喂時(shí)間大口黑鱸攝食、生長(zhǎng)和飼料利用效率Table1 Feed intake,growth and feed utilization efficiency oflargemouth bass fed with differentregimes offeeding and feed deprivation
2.1 大口黑鱸的攝食、生長(zhǎng)和飼料利用效率
從表1可見(jiàn):實(shí)驗(yàn)結(jié)束時(shí)S0組魚(yú)體質(zhì)量和體質(zhì)量增加顯著高于S1和S2組(P<0.05),S1組最終體質(zhì)量和體質(zhì)量增加明顯高于S2組(P<0.05);SGR變化趨勢(shì)與體質(zhì)量增加相同;隨投喂-停喂時(shí)間比例下降,F(xiàn)I和FCR呈下降趨勢(shì),但不同處理組間FI和FCR差異均無(wú)統(tǒng)計(jì)學(xué)意義(P>0.05);不同處理之間NRE和PRE差異也均無(wú)統(tǒng)計(jì)學(xué)意義(P>0.05)。
2.2 大口黑鱸的肥滿度、肝體比和魚(yú)體組成
從表2可見(jiàn):隨投喂-停喂時(shí)間比例的降低,CF、HSI、魚(yú)體粗蛋白質(zhì)和粗脂肪含量均呈下降趨勢(shì),魚(yú)體水分含量呈上升趨勢(shì),但不同處理間差異無(wú)統(tǒng)計(jì)學(xué)意義(P>0.05);S0組實(shí)驗(yàn)魚(yú)體灰分及磷含量在統(tǒng)計(jì)學(xué)上顯著高于S1組(P<0.05),而與S2組間差異無(wú)統(tǒng)計(jì)學(xué)意義(P>0.05)。

表2 不同投喂-停喂時(shí)間大口黑鱸肥滿度、肝體比及魚(yú)體組成Table2 Condition factor,hepatosomatic index and whole body composition oflargemouth bass fed with differentregimes offeeding and feed deprivation
2.3 大口黑鱸的氮、磷廢物排放
從圖1可見(jiàn):交替進(jìn)行投喂和停喂對(duì)氮、磷廢物排放量未產(chǎn)生顯著影響(P>0.05);實(shí)驗(yàn)期間S0、S1和S2組大口黑鱸氮排放量相對(duì)于魚(yú)產(chǎn)量為41.6~44.1 g/kg,磷排放量為11.6~12.2 g/kg。

圖1 不同投喂-停喂時(shí)間大口黑鱸的氮和磷廢物排放Fig.1 Nitrogen(N)and phosphorus(P)waste output of largemouth bass fed with differentregimes offeeding and feed deprivation
3.1 交替投喂-停喂時(shí)大口黑鱸的補(bǔ)償生長(zhǎng)
通常,根據(jù)前期經(jīng)過(guò)營(yíng)養(yǎng)限制的魚(yú)在恢復(fù)營(yíng)養(yǎng)階段的特定生長(zhǎng)率(SGR)和體質(zhì)量與對(duì)照魚(yú)(未受過(guò)營(yíng)養(yǎng)限制)的差異來(lái)判定是否發(fā)生補(bǔ)償生長(zhǎng)以及補(bǔ)償生長(zhǎng)的強(qiáng)度。完全補(bǔ)償指前期經(jīng)過(guò)營(yíng)養(yǎng)限制的魚(yú)在恢復(fù)營(yíng)養(yǎng)階段結(jié)束時(shí)體質(zhì)量與對(duì)照魚(yú)無(wú)顯著差異;部分補(bǔ)償指前期經(jīng)過(guò)營(yíng)養(yǎng)限制的魚(yú)在恢復(fù)營(yíng)養(yǎng)階段結(jié)束時(shí)體質(zhì)量仍明顯低于對(duì)照魚(yú),但在恢復(fù)期間SGR明顯高于對(duì)照魚(yú)[7-8]。在本研究中,S0組魚(yú)飼料系數(shù)和氮保留效率與HUANG等[2]報(bào)道的相關(guān)實(shí)驗(yàn)相比無(wú)顯著差異,說(shuō)明對(duì)照魚(yú)攝食正常。S1和S2組在實(shí)驗(yàn)結(jié)束時(shí)魚(yú)體質(zhì)量明顯低于S0組:表明大口黑鱸經(jīng)過(guò)停喂后再恢復(fù)投喂未實(shí)現(xiàn)完全補(bǔ)償。由于本實(shí)驗(yàn)采用交替投喂和停喂的方法,每次停喂或投喂的時(shí)間較短,難以確定每次停喂結(jié)束時(shí)以及恢復(fù)投喂結(jié)束時(shí)的魚(yú)體質(zhì)量和魚(yú)體組成。假定S1和S2組停喂期間魚(yú)體質(zhì)量未變化(MG=0),根據(jù)實(shí)際投喂時(shí)間(S1組停喂14 d,投喂42 d;S2組停喂7 d,投喂49 d)計(jì)算出S1和S2組投喂期間的SGR分別為(3.4±0.1)%/d和(3.1±0.1)%/d,明顯高于S0組(P<0.05),由此判斷S1和S2組在恢復(fù)投喂期間表現(xiàn)出部分補(bǔ)償生長(zhǎng)。
對(duì)魚(yú)類補(bǔ)償生長(zhǎng)能力的認(rèn)識(shí)至今存在分歧。部分研究表明,一些魚(yú)類種類經(jīng)過(guò)饑餓后在恢復(fù)投喂期間表現(xiàn)出部分補(bǔ)償生長(zhǎng)[11];但另外的研究表明,同種魚(yú)類經(jīng)過(guò)饑餓后恢復(fù)投喂可表現(xiàn)出超補(bǔ)償或完全補(bǔ)償能力,如HAYWARD等[9]報(bào)道,交替投喂-停喂雜交太陽(yáng)魚(yú)時(shí)其體質(zhì)量增加可達(dá)到正常投喂時(shí)的2倍:表明交替停喂-投喂較一次性投喂-停喂有利于誘導(dǎo)補(bǔ)償生長(zhǎng)。CUI等[15]發(fā)現(xiàn),交替停喂-投喂時(shí)銀鯽(Carassius auratus gibelio)未表現(xiàn)出完全補(bǔ)償生長(zhǎng),認(rèn)為采用該種投喂策略不能增強(qiáng)銀鯽的補(bǔ)償生長(zhǎng)。本研究采用2種交替投喂-停喂周期時(shí)大口黑鱸表現(xiàn)出部分補(bǔ)償生長(zhǎng),這與早期對(duì)羅非魚(yú)(Oreochromis niloticus L.)和銀鯽的研究結(jié)論一致[15-20]。S1和S2組投喂期間的體質(zhì)量增加分別為(1.06±0.10)g/d和(1.03±0.10)g/d;鑒于大口黑鱸的體質(zhì)量增加隨著停喂時(shí)間的增加而降低,據(jù)此推算,使魚(yú)產(chǎn)量不至于下降的交替投喂-停喂時(shí)間應(yīng)為每投喂13 d后停喂1 d。
3.2 交替投喂-停喂對(duì)大口黑鱸攝食和飼料利用效率的影響
魚(yú)類實(shí)現(xiàn)補(bǔ)償生長(zhǎng)的機(jī)制包括:1)增加攝食[8,21-22];2)提高食物利用效率[23-24];3)增加攝食和提高食物利用效率[16]。在本研究中,按實(shí)際投喂時(shí)間計(jì)算的S1和S2組的攝食率分別為(2.2±0.6)%/d和(2.3±0.3)%/d,均高于S0組。鑒于S1和S2組的飼料系數(shù)(FCR)和氮保留效率(NRE)與S0組無(wú)顯著差異,可以認(rèn)為在恢復(fù)投喂期間大口黑鱸是通過(guò)增加攝食,而非提高食物利用效率來(lái)實(shí)現(xiàn)補(bǔ)償生長(zhǎng)。整個(gè)實(shí)驗(yàn)期間,S1組和S2組的攝食率和FCR均低于S0組:表明采用交替投喂和停喂的方法有助于降低大口黑鱸養(yǎng)殖中的FCR。
3.3 交替投喂-停喂對(duì)大口黑鱸魚(yú)體形態(tài)和組成的影響
魚(yú)類饑餓時(shí)會(huì)利用體內(nèi)貯存的蛋白質(zhì)、脂肪和碳水化合物來(lái)提供能量[6]。CUI等[20]報(bào)道:銀鯽在饑餓的第1周內(nèi)主要利用脂肪提供代謝能量,隨饑餓時(shí)間延長(zhǎng)魚(yú)體脂肪含量迅速下降,而蛋白質(zhì)消耗速率保持相對(duì)恒定;當(dāng)魚(yú)體蛋白質(zhì)消耗量超過(guò)脂肪消耗量時(shí)耗氧率降低至最低點(diǎn)。王巖[16]報(bào)道,魚(yú)類在補(bǔ)償生長(zhǎng)期間魚(yú)體組成恢復(fù)往往先于體質(zhì)量恢復(fù)。在本研究中,實(shí)驗(yàn)結(jié)束時(shí)S1和S2組肥滿度、肝體比、全魚(yú)粗蛋白質(zhì)和粗脂肪含量與S0組無(wú)顯著差異,表明交替投喂3 d停喂1 d或交替投喂7 d停喂1 d未導(dǎo)致大口黑鱸魚(yú)體形態(tài)和全魚(yú)組成發(fā)生顯著變化;而S2組全魚(yú)磷含量低于S0組,表明交替投喂3 d停喂1 d可導(dǎo)致魚(yú)體內(nèi)磷的流失。至于長(zhǎng)期交替投喂-停喂是否會(huì)影響大口黑鱸體內(nèi)磷含量有待進(jìn)一步的實(shí)驗(yàn)檢驗(yàn)。
3.4 交替投喂-停喂對(duì)大口黑鱸氮、磷廢物排放的影響
HUANG等[2]報(bào)道,在不同飼料蛋白質(zhì)和脂肪水平下大口黑鱸氮排放和磷排放分別為43~56 g/kg和10~16 g/kg,認(rèn)為大口黑鱸在養(yǎng)殖中的氮廢物排放量低于多數(shù)溫水性海水魚(yú)類(氮排放往往超過(guò)50 g/kg)。在本研究中,大口黑鱸氮排放為41.6~44.1 g/kg,磷排放為11.6~12.2 g/kg,與前期研究[3]結(jié)果接近,進(jìn)一步證實(shí)了投喂配合飼料時(shí)大口黑鱸的氮、磷廢物排放量較低。S1和S2組大口黑鱸氮排放和磷排放略低于S0組:表明采用交替投喂-停喂策略可降低大口黑鱸的氮、磷排放量,有利于減輕大口黑鱸養(yǎng)殖水體內(nèi)氮、磷廢物的積累。
本文研究了不同投喂-停喂時(shí)間對(duì)大口黑鱸攝食、生長(zhǎng)、食物利用、魚(yú)體組成和氮、磷廢物排放的影響。結(jié)果表明,采用交替投喂-停喂方法可影響大口黑鱸的攝食率、體質(zhì)量增加、飼料系數(shù)、飼料氮和磷廢物排放,并且該影響與投喂-停喂時(shí)間的比例有關(guān)。在實(shí)際生產(chǎn)中,通過(guò)利用補(bǔ)償生長(zhǎng)原理,可以適當(dāng)改進(jìn)大口黑鱸投喂技術(shù),以期獲得更好的生產(chǎn)效益。根據(jù)本實(shí)驗(yàn)結(jié)果,當(dāng)在大口黑鱸池塘養(yǎng)殖中采用交替投喂-停喂策略時(shí),合理的停喂-投喂時(shí)間應(yīng)為投喂13 d停喂1 d。
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Effect of different feeding-feed deprivation time on feed intake,growth and waste output of largemouth bass(Micropterus salmoides).Journal of Zhejiang University(Agric.&Life Sci.),2017,43(3):359-364
HUANG Di1,REN Xing2,WU Yubo1,CHEN Jianming3,WANG Yan2*
(1.College of Animal Sciences,Zhejiang University, Hangzhou 310058,China;2.Ocean College,Zhejiang University,Zhoushan 316021,Zhejiang,China;3.Key Laboratory of Fish Health and Nutrition of Zhejiang Province,Zhejiang Institute of Freshwater Fisheries,Huzhou 313001,Zhejiang,China)
compensatory growth;feeding regime;body massgain;feed conversion ratio;waste output
):黃迪(http://orcid.org/0000-0002-5075-4535),E-mail:huangdi0710@sina.com
2016-07-12;接受日期(Accepted):2016-10-27
S 963.165
A
10.3785/j.issn.1008-9209.2016.07.121
浙江省科技廳重點(diǎn)項(xiàng)目(2015C32003);浙江省淡水水產(chǎn)研究所農(nóng)業(yè)部淡水漁業(yè)健康養(yǎng)殖重點(diǎn)實(shí)驗(yàn)室開(kāi)放基金項(xiàng)目(ZJK2014001;ZJK2015001)。
*通信作者(Corresponding author):王巖(http://orcid.org/0000-0003-2342-591X),E-mail:ywang@zju.edu.cn
(
浙江大學(xué)學(xué)報(bào)(農(nóng)業(yè)與生命科學(xué)版)2017年3期