13.01.2015 Views

Development of captive broodstock of the grey mullet, Mugil cephalus

Development of captive broodstock of the grey mullet, Mugil cephalus

Development of captive broodstock of the grey mullet, Mugil cephalus

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

Indtan J Fish, 4712) : 91-96, A~K-Jun., 2000<br />

<strong>Development</strong> <strong>of</strong> <strong>captive</strong> <strong>broodstock</strong> <strong>of</strong> <strong>the</strong> <strong>grey</strong> <strong>mullet</strong>,<br />

<strong>Mugil</strong> <strong>cephalus</strong> (L)<br />

MATHEW ABRAHAM, M. KAILASAM, P. KTSHORE CHANDRA, P. SIHRANEE,<br />

K.V. RAJENDRAN AND A.V.K. CKARLES<br />

Central Institute <strong>of</strong> Brackishwater Aquaculture,<br />

Chennaz-600 008, India<br />

ABSTRACT<br />

A <strong>captive</strong> <strong>broodstock</strong> <strong>of</strong> <strong>the</strong> <strong>grey</strong> <strong>mullet</strong> <strong>Mugil</strong> <strong>cephalus</strong> has been successfully<br />

developed at Muttukadu experimental station <strong>of</strong> <strong>the</strong> Central Institute <strong>of</strong><br />

Brackishwater Aquaculture. A stock <strong>of</strong> 72 sub-adult and adult fish in <strong>the</strong> size<br />

range <strong>of</strong> 290-450 mm/300-1,200 g procured from <strong>the</strong> commercial catches were<br />

maintained in 100 tonne capacity RCC tanks hom January '96. During 1996, about<br />

20% <strong>of</strong> <strong>the</strong> stock, both males and females attained final maturity. In 1997, about<br />

60% <strong>of</strong> <strong>the</strong> females and 80% <strong>of</strong> <strong>the</strong> males attained final maturity In mature females<br />

ova diameter <strong>of</strong> <strong>the</strong> matured oocytes ranged from 525 to 614 pa and <strong>the</strong> mature<br />

males were in oozing stage.<br />

Introduction<br />

Brackishwater aquaculture sector<br />

in India which is shrimp dependent has<br />

witnessed set backs <strong>of</strong> late due to<br />

disease outbreaks and environmental<br />

problems and <strong>the</strong>refore <strong>the</strong> need <strong>of</strong> <strong>the</strong><br />

hour is to adopt eco-friendly farming<br />

with emphasis on species diversification.<br />

The striped <strong>mullet</strong>, <strong>Mugil</strong><br />

<strong>cephalus</strong> (L) is one <strong>of</strong> <strong>the</strong> most popular<br />

and fast growing brackishwater finfish<br />

being cultured in tropical and subtropical<br />

regions (Thompson, 1963). The<br />

advantages <strong>of</strong> this species for aquaculture<br />

have been well documented<br />

(Odum, 1970; Pillai et al., 1984 and<br />

Rajyalakshmi and Chandra, 1987). In<br />

India farming <strong>of</strong> this species is being<br />

done mainly by polyculture method<br />

using seed collected from <strong>the</strong> wild and<br />

is restricted to traditional system. Seed<br />

availability from <strong>the</strong> nature is erratic<br />

and undependable. Seed production by<br />

induced breeding in captivity is <strong>the</strong><br />

only alternative to promote <strong>the</strong> farming<br />

<strong>of</strong> this species. Though breeders are<br />

available from <strong>the</strong> commercial catches,<br />

induced breeding and seed production<br />

have not been accomplished so far<br />

eventhough several efforts have been<br />

made. This is mainly because <strong>of</strong> <strong>the</strong><br />

problems associated with <strong>the</strong> procurement,<br />

transport and acclimatization <strong>of</strong><br />

<strong>the</strong> breeders (Ma<strong>the</strong>w, et al., 1998).<br />

Hence it is absolutely necessary to<br />

maintain and develop <strong>captive</strong> <strong>broodstock</strong><br />

to facilitate induced breeding and seed<br />

production <strong>of</strong> captivity. The paper<br />

presents <strong>the</strong> details <strong>of</strong> <strong>the</strong> development<br />

<strong>of</strong> a <strong>captive</strong> <strong>broodstock</strong> cf M~tgil<br />

<strong>cephalus</strong> at <strong>the</strong> field centre <strong>of</strong> <strong>the</strong><br />

Central Institute <strong>of</strong> Brackishwater<br />

Aquaculture at Muttukadu, for <strong>the</strong> first<br />

time in <strong>the</strong> country.


Materials and methods<br />

Adult and sub-adult fishes caught<br />

aiive in <strong>the</strong> commercial catches at<br />

Muttukadu and Kovaiam which are<br />

devoid <strong>of</strong> any visible injuries were<br />

proc~red and transported to <strong>the</strong> hatchery<br />

complex at Muttukadu in plastic<br />

tubs having seawater with aeration<br />

during December 1995. They uTere<br />

trest,d vith 1.0 ppm acr~flavine for an<br />

hmr. They wee <strong>the</strong>n released in 20<br />

tome capacity tanks havzllg water<br />

treats: with calcium hypochlorite<br />

(Mz<strong>the</strong>w t al., 1998). The fishes were<br />

retained or 3 days and t'he survived<br />

ones were trarderi-ed to <strong>the</strong> <strong>broodstock</strong><br />

holding tanks. ,Among about 130 fishes<br />

procured 72 have survived. These<br />

fishes were in <strong>the</strong> size range <strong>of</strong> 290-450<br />

nlm and 300-1:200 g.<br />

7% b~oodstock was maintained in<br />

t\b.o 100 s capacity RCC tanks having<br />

raciiiiy for seawater circulation. Water<br />

exchange was done daily @ 1580%. The<br />

tanks were cleaned every alternate uay<br />

to flush out <strong>the</strong> faecal matter and<br />

debris. Tne fishes were fed with a<br />

formuiated peileted rnatcration feed @<br />

3% <strong>of</strong> body weight daily During 1996-<br />

'97 <strong>the</strong>y were %d with a high lipid feed<br />

having <strong>the</strong> prosimate compositiun <strong>of</strong><br />

35.30% crude proLeh, 6.0% crude lipid,<br />

3.318 trude fibre, 8.79% ash, 5.47%<br />

moisture azid 41.138 NPE. Eventhough<br />

<strong>the</strong> fishes have grown well and were in<br />

goo& health <strong>the</strong> percentage <strong>of</strong> maturity<br />

was only 30. When few fishes were<br />

dissected and examined. it was found<br />

that <strong>the</strong>re was an excess accumulation<br />

<strong>of</strong> fat in <strong>the</strong> coe:o;rr.ic cavity and aroznd<br />

<strong>the</strong> intessi~e. It is believed that this<br />

ercw faz accumulaticn xighht have<br />

lnterferad with 'he gonadial maturity.<br />

Considering this, two types <strong>of</strong> feeds<br />

\.;.cw 1 sc.3 difring 1997-'98. A high lipid<br />

feed having <strong>the</strong> proximate con~positio::<br />

<strong>of</strong> 3S.08 crude protein, 8.2% crude lipid,<br />

4.47% crude fibre, 14.58% total ash and<br />

7.35% moisture was fed during <strong>the</strong><br />

recouping period (January to August)<br />

and a low lipid feed having <strong>the</strong><br />

proximate composition <strong>of</strong> 34.05% crude<br />

protein, 4.54% crude lipid, 12.22% total<br />

ash and 5.91% moisturc was fed during<br />

<strong>the</strong> gonadial development period<br />

(September-December). The fishes were<br />

also foznd to be feeding on <strong>the</strong> tenthic<br />

algal ccimmmlty that were allowed to<br />

grow on <strong>the</strong> wails <strong>of</strong> <strong>the</strong> tanks. Water<br />

quality parameters like salinity, pH,<br />

temperature, dissolved oxygen, turbidity,<br />

ammonia and nitrite were estimated<br />

at weekly<br />

The fishes were<br />

examined once in a month to monitor<br />

<strong>the</strong>ir health condition. Maturity <strong>of</strong><br />

ft\males was examined by - gonadial -<br />

biopsy using a ca<strong>the</strong>ter. In <strong>the</strong> case <strong>of</strong><br />

males, ths abdomen was gently pressed<br />

ro see <strong>the</strong> presence <strong>of</strong> milt. Rshes were<br />

anes<strong>the</strong>tised before handlizlg.<br />

The monthly average values <strong>of</strong><br />

salinity, pH, dissolved oxygen, temperature,<br />

turbidity and ammonia are shown<br />

in Fig. 1. Variation in <strong>the</strong> salinity<br />

during <strong>the</strong> period was not much 2nd<br />

was limited to 5.2 ppt. Maximum<br />

salinity <strong>of</strong> 32.2 ppt was noted dluring<br />

May '97 and <strong>the</strong> lowest salinity <strong>of</strong> 27.0<br />

ppt was recorded during January, 1998.<br />

The pH <strong>of</strong> <strong>the</strong> water also did not vary<br />

much and <strong>the</strong> water always remained<br />

alkaline. Minimum pH was 7.6 and <strong>the</strong><br />

maximum was 8.3. Minimum dissolved<br />

oxygen <strong>of</strong> 6.8 ppm was during July and<br />

throughout <strong>the</strong> period <strong>the</strong>re was no sign<br />

<strong>of</strong> oxygen depletion. Water temperature<br />

ranged between 28.5% during January<br />

'98 and 32.g°C during June '97. Turbidity<br />

vdues indicate that <strong>the</strong> water


Deuelopment <strong>of</strong> brood stock <strong>of</strong> <strong>Mugil</strong> <strong>cephalus</strong> 93<br />

SALINITY<br />

36 , .-4<br />

71 . . . . I<br />

M A M J J U A S O N D J F<br />

g 7.2 --<br />

DISSOLVED OXYGEN<br />

64 1, 1<br />

M A M J J U A S O N D J F<br />

TEMPERATURE<br />

161 , , , . . , . . , , , 1<br />

M A M J J U A S O N D J F<br />

01 , , , i<br />

M A M J J U A S O N D J F<br />

AMMONIA<br />

r - P<br />

0 J<br />

M A M J J U A S O N D J F<br />

MONTHS<br />

Fig. 1. Monthly average values <strong>of</strong> water qua1il;Sparameters<br />

in <strong>broodstock</strong> tanks during<br />

1996-'97.<br />

remained almost clear throughout <strong>the</strong><br />

period because <strong>of</strong> daily water exchange.<br />

Similarly ammonia content also remained<br />

to be low due to regular water<br />

exchange. It was seen that <strong>the</strong> water<br />

quality parameters did not vary much<br />

during <strong>the</strong> <strong>broodstock</strong> development<br />

period.<br />

The <strong>broodstock</strong> fishes were examiaed<br />

at regular intervals to monitor<br />

<strong>the</strong>ir health condition. The fishes were<br />

examined for ecto-parasites mainly in<br />

<strong>the</strong> gdls and body surface. Parasitic<br />

organisms were found to cause major<br />

problems in <strong>captive</strong> <strong>broodstock</strong> development.<br />

This can be attributed to <strong>the</strong><br />

presence <strong>of</strong> natural parasitic fauna in<br />

<strong>the</strong> wild caught fish and <strong>the</strong>ir f~rthsr<br />

proliferation in captivity. Once thp<br />

fishes were found to be infected with<br />

Lernanthropus sp. it was effectively<br />

treated with Dichlorvos @ 1 ppm for one<br />

hour, On few o<strong>the</strong>r occasions <strong>the</strong> fishes<br />

were found to be infected with Caligus<br />

sp. and treatment with formalin @ 100<br />

ppm for 90 minutes was found to be<br />

verjj effective. Later on to prevent<br />

infections, <strong>the</strong> <strong>broodstock</strong> holding tanks<br />

were treated at monthly intervals with<br />

formalin @ 100 ppm for one hour as a<br />

prophylactic measure and infections<br />

were minimised later on. Normallv <strong>the</strong><br />

treatments are done after reducing <strong>the</strong><br />

water level to 25 cm and also under<br />

close watch. Whenever <strong>the</strong> fish showed<br />

signs <strong>of</strong> stress during treatment, <strong>the</strong><br />

water was exchanged immediately. It<br />

is very essential that <strong>the</strong> stock should<br />

be maintained free <strong>of</strong> parasites for <strong>the</strong>ir<br />

survival and gonadial maturation.<br />

Gonadial maturity <strong>of</strong> <strong>the</strong> stock was<br />

examined at monthly intervals dcring<br />

September and October and at fortnightly<br />

intervals during November-<br />

February by random sampling. The<br />

state <strong>of</strong> ovarian maturity was assessed<br />

by <strong>the</strong> in vivo monitoring method<br />

validated by Shehadeh et al., (1973). A<br />

ca<strong>the</strong>ter <strong>of</strong> 1.5 mm O.D. was used. One


Ma<strong>the</strong>w Abraham et al. 94<br />

Fig. 2. Percentage occurrence <strong>of</strong> different maturity<br />

stiiges in II.fugil <strong>cephalus</strong> females during<br />

1997.<br />

end <strong>of</strong> <strong>the</strong> ca<strong>the</strong>ter was inserted through<br />

<strong>the</strong> oviduct to 5.8 cm and <strong>the</strong> o<strong>the</strong>r end<br />

<strong>of</strong> <strong>the</strong> ca<strong>the</strong>ter was held in <strong>the</strong> mouth<br />

<strong>of</strong> <strong>the</strong> operator and aspirated while<br />

slowly withdrawing <strong>the</strong> ca<strong>the</strong>ter. The<br />

oocytes in <strong>the</strong> ca<strong>the</strong>ter was blown out<br />

to a petridish having 2% formalin. The<br />

oocytes were examined under microscope<br />

and <strong>the</strong> ova diameter measured<br />

using calibrated ocular micrometer. In<br />

<strong>the</strong> case <strong>of</strong> males, <strong>the</strong> presence <strong>of</strong> milt<br />

was physicaliy examined by pressing<br />

<strong>the</strong> abdomen. The percentage occurrence<br />

<strong>of</strong> female and male fishes in<br />

different mon4hs was assessed and is<br />

depicted in Fig. 2&3. All <strong>the</strong> females<br />

were in immature stage upto September.<br />

Initiation <strong>of</strong> maturation was observed<br />

during October and about 50%<br />

<strong>of</strong> <strong>the</strong> females were in maturing stage<br />

with ova diameter ranging fom 200-300<br />

pm. The remaining 50% were in immature<br />

stage. In <strong>the</strong> succeeding month,<br />

females showed increasing trend in<br />

ovarian development and about 25% <strong>of</strong><br />

<strong>the</strong> females were in mature stage with<br />

ova diameter ranging from 450-540 pm.<br />

The remaining 30% were immature and<br />

45% were in maturing stage. During<br />

December <strong>the</strong> percentage occurrence <strong>of</strong><br />

mature females increased and was 50%.<br />

Out <strong>of</strong> <strong>the</strong> remaining 50%, 25% were<br />

immature and 25% were in maturing<br />

stage. During January, 25% were<br />

immature, 25% in mature and 50% in<br />

resorption stages. During February, all<br />

<strong>the</strong> females were ei<strong>the</strong>r immature or in<br />

resorption stages. Mature eggs were<br />

non-adhesive, round with tertiary yolk<br />

globule and measured 525 pm or more<br />

in diameter.<br />

In <strong>the</strong> case <strong>of</strong> males, dl were in<br />

immature stage during August. Initiation<br />

<strong>of</strong> maturation was observed in <strong>the</strong><br />

first week <strong>of</strong> September and almost 75%<br />

<strong>of</strong> <strong>the</strong> males were in maturing stage<br />

during this month. In October aboat<br />

25% were in immature stage, 15% in<br />

maturing stage and 60% in mature<br />

stage. Maximum number <strong>of</strong> oozing<br />

mature males (65%) were observed<br />

during November. The percentage <strong>of</strong><br />

mature males drastically declined to<br />

15% in December and about 65% males<br />

lost <strong>the</strong> condition and were in resorption<br />

stage and in January only 5% were<br />

in mature stage. During February, all<br />

were ei<strong>the</strong>r immature or in resorption<br />

conditon.<br />

From a scrutiny <strong>of</strong> <strong>the</strong> percentage<br />

occurrence <strong>of</strong> mature females and<br />

males, it is seen that majority <strong>of</strong> males<br />

attained maturitv durinq November<br />

Fig. 3. Percentage occurrence <strong>of</strong> different maturity<br />

stages in <strong>Mugil</strong> <strong>cephalus</strong> males during<br />

1997.


Derelopment <strong>of</strong> brood stock <strong>of</strong> <strong>Mugil</strong> <strong>cephalus</strong> 95<br />

and females during December. The<br />

maturation <strong>of</strong> females and males is not<br />

synchronizing and majority <strong>of</strong> males<br />

attained maturity almost a month<br />

earlier to females. In <strong>the</strong> commercial<br />

catches also it is observed that <strong>the</strong><br />

mature males start appearing as early<br />

as from October onwards and females<br />

through in few numbers, start appearing<br />

from November onwards.<br />

A prerequisite for propagation <strong>of</strong> a<br />

fish species is <strong>the</strong> mature <strong>broodstock</strong>.<br />

In <strong>the</strong> past, researchers had to rely<br />

solely on nature for breeders. To<br />

overcome this, efforts have been made<br />

to develop <strong>captive</strong> broostocks and<br />

success have been reported. Liao et at.<br />

(1971) have developed a <strong>captive</strong><br />

<strong>broodstock</strong> ir, freshwater and succeeded<br />

in breeding <strong>the</strong>m after acclimatising<br />

<strong>the</strong>m to seawater three months ~rior to<br />

breeding. Shehadeh et al. (1973) have<br />

maintained three year old <strong>mullet</strong> in<br />

pond with seawater and provision for<br />

<strong>the</strong> growth <strong>of</strong> benthic diatom and<br />

algae. The fishes have attained<br />

maturity in <strong>the</strong> following year. By<br />

manipuIating photoperiod and ambient<br />

water temperature, it has been shown<br />

that reproductive cycle can be accelerated<br />

(Kuo et al., 1974). It has been<br />

noted that <strong>the</strong> onset <strong>of</strong> vitellogenesis is<br />

regulated by environmental conditions.<br />

A sliortened photoperiod (6L118D) initiates<br />

vitcellogenesis and a lower<br />

temperature (2I0C) ensures its completion.<br />

Fishes that have been matured<br />

through environmental manipulations<br />

have been successfully induced to<br />

spawn outside <strong>the</strong> normal breeding<br />

season.<br />

and Training Centre, <strong>broodstock</strong>s are<br />

devleloped in concrete raceways<br />

equipped with constant flow <strong>of</strong> water.<br />

The fishes were fed with formulated<br />

feed having 36.0% protein and 4.1% fat,<br />

@ 3% <strong>of</strong> body weight daily (Tarnaru et<br />

al., 1993). Outdoor rectangular rubberlined<br />

ponds and round concrete ponds<br />

are used at <strong>the</strong> Oceanic Institute,<br />

Hawaii for <strong>broodstock</strong> development.<br />

Here fishes were fed on <strong>the</strong> naturally<br />

occurring benthic growth and were also<br />

given Purina Trout Chow as supplementary<br />

feed (Lee et al., 1988; 1992). It<br />

has also been reported that striped<br />

<strong>mullet</strong> females have matured in outdoor<br />

seawatnr or brackishwater tanks and<br />

indoor seawater tanks (Tamaru et al.,<br />

1991). Salinites ranging from 13-35 ppt<br />

are adequate for ovarian maturation in<br />

<strong>captive</strong> <strong>mullet</strong> females<br />

The present study has demonstrated<br />

that majority <strong>of</strong> <strong>the</strong> <strong>broodstock</strong><br />

can attain maturity provided <strong>the</strong>y are<br />

maintained with regular water exchange<br />

and feeding. Fceding <strong>the</strong> stock<br />

with a maturation feed <strong>of</strong> high lipid<br />

content (8.2%) during <strong>the</strong> recouping<br />

period and feeding with a low lipid<br />

(4.54%) during <strong>the</strong> gonad maturation<br />

period was found to be more effective<br />

to get more fishes matured. The<br />

salinity <strong>of</strong> <strong>the</strong> <strong>broodstock</strong> tanks ranged<br />

from 27.0-32.2 ppt. Since <strong>the</strong> salinity<br />

range was not significant, it is difficult<br />

to draw conclusion on <strong>the</strong> effect <strong>of</strong><br />

salinity on maturation. However, it is<br />

observed that <strong>the</strong> period <strong>of</strong> maturation<br />

coincides with a shortened day and a<br />

decrease in <strong>the</strong> water temperature.<br />

Hence it is evident that a shortened<br />

Implantation <strong>of</strong> hormone pellets for photoperiod may help initiate vitelloaccelerating<br />

maturation was found to be genesis and a lower temperature hdps<br />

effective in milk fish (Lee et al., 1986). its completion as already observed in<br />

At Guam Aquaculture <strong>Development</strong> earlier reports.


Acknowledgments<br />

The authors are indebted to Dr.<br />

G.R.M. Rao, Director, CIBA and to Dr.<br />

K. Alagarswami, former Director, CIBA<br />

for <strong>the</strong>ir encouragements during <strong>the</strong><br />

course <strong>of</strong> this study<br />

References<br />

Kuo, C.M., C.E. Nash and Z.H. Shehadeh 1974.<br />

The effects <strong>of</strong> temperature and photoperiod<br />

on ovarian development in <strong>captive</strong><br />

<strong>grey</strong> <strong>mullet</strong> (<strong>Mugil</strong> cephal~ls L.). Aquaculture,<br />

3 : 25-43.<br />

Lee, C.S., C.S. Tamaru, J.E. Banno and C.D.<br />

Kelley 1986. Influence <strong>of</strong> chronic administration<br />

<strong>of</strong> LIIRII-analogue andlor 17 -<br />

methyltestosterone on maturation in<br />

mi& fish, Chanos chanos. Aquaculture,<br />

59 : 147-159.<br />

Lee, C.S., C.S. Tamaru and C.D. Kelley 1988.<br />

The cost and effectiveness <strong>of</strong> CPII HCG<br />

and LHRH-a on <strong>the</strong> induced spawning <strong>of</strong><br />

<strong>grey</strong> <strong>mullet</strong>, <strong>Mugil</strong> <strong>cephalus</strong>. Aquaculture,<br />

73 : 341-347.<br />

Lee, C.S., C.S. Tamaru, C.D. Kelley, A.<br />

Morinaka and G.T. Miyamoto 1992. The<br />

effect <strong>of</strong> salinity on <strong>the</strong> induction <strong>of</strong><br />

spawning and fertilization il <strong>the</strong> striped<br />

<strong>mullet</strong>: <strong>Mugil</strong> <strong>cephalus</strong>. Aquaculture,<br />

102 : 289-296.<br />

Liao, I.C., D.L. Lee, M.Y. Lim and M.C. Lo<br />

1971. Preliminary report on induced<br />

breeding <strong>of</strong> pond reared <strong>mullet</strong> (<strong>Mugil</strong><br />

<strong>cephalus</strong> L.). Fish. Sex Chindm. Jt.<br />

Comm. Rul: Reconstr, 11 : 30-35.<br />

Ma<strong>the</strong>w Abraham: P.K Chandra, M. Kailasam<br />

and V.K. Char!es 1998. Acclimatization<br />

cf <strong>Mugil</strong> <strong>cephalus</strong> (L) procured from<br />

commercial catches. Indian J Fish.,<br />

45(2) : 217-219.<br />

Odum, RE. 1970. Utilization <strong>of</strong> <strong>the</strong> direct<br />

gazing and plant detritus food chains by<br />

<strong>the</strong> striped <strong>mullet</strong>, <strong>Mugil</strong> <strong>cephalus</strong>. In:<br />

Marine Food Chains. J.H. Steels, Oliver<br />

and Boyd (Eds.), Edinburgh, Scotland.<br />

Pillai, S.M., P.K. Ghosh, T Rajyalakshmi and<br />

AK. Roy 1984. Observation on growth,<br />

survival and production <strong>of</strong> <strong>grey</strong> <strong>mullet</strong>s,<br />

<strong>Mugil</strong> <strong>cephalus</strong> (L), Liza parsia<br />

(Hamilton! and Liza tade (Forsskal) in a<br />

coastal low saline polyculture pond. Proc.<br />

Symp. Coastal Aquacult., 3 : 776-781.<br />

Rajyalakshmi, T. and D.M. Chandra 1987.<br />

Recruitment in nature and growth in<br />

brackishwater ponds <strong>of</strong> <strong>the</strong> striped<br />

mdet <strong>Mugil</strong> <strong>cephalus</strong> L. in Andhra<br />

Pradesh, India, Indian tl: .-lnim. Sci.,<br />

57(3) : 229-240.<br />

Shehadeh, Z.H., C.M. Kuo and C.E. Nash 1973.<br />

Establishing <strong>broodstock</strong> <strong>of</strong> <strong>grey</strong> <strong>mullet</strong><br />

(<strong>Mugil</strong> <strong>cephalus</strong> L.) in small ponds.<br />

Aquaculture, 2 : 379-384.<br />

Tamaru, C.S., C.S. Lee and H. Ako 1991.<br />

Improving <strong>the</strong> larval rearing <strong>of</strong> striped<br />

<strong>mullet</strong> (<strong>Mugil</strong> <strong>cephalus</strong>) by manipulating<br />

quality and quantity <strong>of</strong> <strong>the</strong> rotifer,<br />

Brachionus plicatilis. In: Rotifer and<br />

Microalgae Culture Systems. Proc. <strong>of</strong> a<br />

M.S. - Asia Workshop. W. Mks and K.<br />

Main (Eds.), The Oceanic Institute,<br />

Honolulu, p. 89-103.<br />

Tamax-!!, C.S., W.J.F. Gerald Jr. and Y Sat0<br />

1993. Hatchery Manual for <strong>the</strong> Artificial<br />

Propagation <strong>of</strong> Striped Mullet (<strong>Mugil</strong><br />

<strong>cephalus</strong>). 167 pp. Department <strong>of</strong> Commerce,<br />

Suite 601, G.I.T.C. Rldg., 590<br />

South Marine Drive, Tamuning, Guam-<br />

95911.<br />

Tamam, C.S., C.S. Leel, C.D. Kelley, G<br />

hliyarnoto and A. moriwake 1994. Oocyte<br />

growth in striped <strong>mullet</strong>, <strong>Mugil</strong> <strong>cephalus</strong><br />

(L) maturing at different salinites. d<br />

World Aquaculture Society, 225(1) : 109-<br />

115.<br />

Thompson, J.M. 1963. Synopsis <strong>of</strong> biological<br />

data on <strong>the</strong> <strong>grey</strong> <strong>mullet</strong> (<strong>Mugil</strong> <strong>cephalus</strong><br />

L). Fish Symp. Div. Oceanogr, C.S. I.R.O.,<br />

Australia, (1).

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!