D om e st ica t ion of Ce le be s r a in bow fish
( M a r osa t h e r in a la dige si)
1
Jayadi Jayadi, 1 Am rah Husm a, 2 Nursahran, 3 Ardiansyah, 3 Sriwahidah
1
Depart m ent of Aquacult ure, Faculty of Fishery and Marine Science, I ndonesia Muslim
University, Makassar, I ndonesia; 2 Depart m ent of Aquacult ure, College of Marine
Sciences and Fisheries, Balikdiw a, Makassar, I ndonesia; 3 Depart m ent of Aquacult ure,
Agricult ural Polyt echnic St ate of Pangkep, Pangkaj enne and Kepulauan, I ndonesia.
Corresponding aut hor: J. Jayadi, j ayadi_fat rial@yahoo.com
Abst r a ct . I n t his r esearch, dom esticat ion of Celebes r ainbow fish ( Mar osat herina ladigesi) was st art ed
fr om t he br oodst ock r ear ing, spawning and lar val r ear ing. The pur pose of t his st udy was t o det er m ine
t he sur vival r at e, fecundit y r at e, and gonad m at ur it y levels of t he br oodst ock t hat was fed live feed;
Daphnia sp., Chir onom us sp., and Culex sp., wher eas dur ing t he spawning per iod, t he t ot al num ber of
eggs; t he num ber of eggs hat ching; egg incubat ion t im e; t he num ber of unhat ched eggs; and hat ching
r at e wer e evaluat ed. The aim of st udy in t he lar val r ear ing is t o det er m ine t he sur vival r at e of t he lar va.
Br oodst ocks of M. ladigesi wer e collect ed fr om Bant im ur ung r iver and Pat unung Asue River of Mar os
r egency; Jennae River and Gowalor ong River of Pangkaj enne Kepulauan r egency; Asanae River of Bone
r egency. The r esult of r esear ch dem onst r at ed t hat sur vival r at es of br oodst ocks fed Dapnia sp.,
Chir onom us sp., and Culex sp. wer e 91% , 86% , 81% , r espect ively. Br oodst ocks of M. ladigesi t hat wer e
fed Daphnia sp. pr oduced t he highest num ber of eggs ( 849) , wit h t he hat ching r at e of 70.77% , wher eas
t he br oodst ocks t hat wer e fed Chir onom us sp. pr oduced 595 eggs, wit h t he hat ching r at e of 67.11% ,
and t he br oodst ocks t hat wer e fed lar vae of Culex sp. obt ained 565 eggs wit h t he hat ching r at e of
65.14% . The incubat ion per iod was 8- 9 days. The lar vae wer e given nauplius of Daphnia sp. can achieve
t he sur vival r at e of lar vae was 38.31- 39.02% unt il age 5 days, 62.44- 71.67% at 10 days, 20- 30 days
aft er hat ching, t he sur vival r at es r anged fr om 73.06- 99.84% .
Ke y W or ds: Mar osat her ina ladigesi, br oodst ock r earing, spawning, lar val r ear ing, hat ching r at e, sur vival
r at e.
I n t r odu ct ion. I n Sout h Sulaw esi province of I ndonesia, several species of native
freshw at er fish and endem ic fish of t he fam ily Telm at herinidae are found such as
Marosat herina ladigesi, Telm at herina ant oniae, T. albolabiosus, T. bont i, T. celebensis, T.
obscura, T. prognat ha, T. w ahj ui, T. sarasinorum , T. opudi, and T. abendanoni ( Parent i
2011) . One species t hat has been list ed in t he I nt ernat ional Union for Conservat ion of
Nat ure ( I UNC) since 1990 due t o t he t hreat of extinction is M. ladigesi ( Kot t elat 1996;
I UNC 1996) . Based on t he BLAST- N gene analysis w it h t he 99% sim ilarity index ( Jayadi
et al 2015) , M. ladigesi is t he new valid synonim e nam e for form er Telm at herina ladigesi
( Kot t elat et al 1993; Parent i 2011) . The fish is locally know ns as "beseng- beseng" w hile
t he t rade nam e is Celebes rainbow fish. This fish has been cat egorized as endangered
fish in t heir nat ural habit at s ( Anonim 2012) . I n t he recent years, t he fish is only found in
Bant im urung river at Maros regency, Saw ae river at Bone regency, Jenae river at
Pangkaj enne and Kepulauan regency, Asanae river at Soppeng regency ( Jayadi et al
2016) , Pat t unung Asue River at Maros regency ( Karyant i et al 2014) . The fish scarcity in
nat ure due t o t he cont inuous use of pest icides in t he paddy fields, overfishing, and
dest ruction of t heir nat ural habit at s ( Said & Haryani 2011) . M. ladigesi t hat st ill survive in
t he w ild have ext rem ely low levels of genet ic diversit y ( Jayadi et al 2015) . Thus t his
condition m ay furt her exacerbat e it s exist ence in nat ure.
M. ladigesi is know n as freshw at er ornam ent al fish t hat has im port ant econom ic
value ( Kott ellat et al 1993; Andriani 2000; Said et al 2005; Nasut ion et al 2006; Said &
Mayasari 2007; Parent i 2011; Jayadi et al 2013, 2015) , because it s highly at t ractive
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appearance, especially t he m ales. Hence, M. ladigesi is still sought via online t rade
( Hardiat y 2007) . This fish is also still dem anded from businessm en of ornam ent al fish
from t he int erview wit h fisherm en in Maros ( Jayadi et al 2013) . How ever, t hey cannot
m eet t he dem and due t o declined population of t he w ild- caught fish from it s habit at ( Said
& Haryani 2011; Kariyant i et al 2014; Jayadi et al 2013) . The exploit ation rat es ( E) of M.
ladigesi have exceeded t he opt im um lim it of 0.0919 in Bant im urung river ( Bahrul 2014) ,
and in Jennae river and Gow a Lorong river of 0.935 ( Jayadi et al 2016) .
M. ladigesi is an endem ic fish t hat m ay be extinct in t he wild because t he spread
of t he fish is very lim it ed and only found in several rivers in Sout h Sulaw esi, I ndonesia
( Kot t elat et al 1993; Kot t elat 1996; Said et al 2005; Said & Haryani 2011; Jayadi et al
2013) . To ensure t he sust ainabilit y of fish st ocks in nat ure and t o m eet t he supply for
ornam ent al fish, dom estication of M. ladigesi is required t o produce seeds (larvae and
j uvenile), w hich in t urn can prevent t he extinction of t his fish in t he wild.
St udies have been done on M. ladigesi such as bio- ecology, m orphology, and
karyot ype ( Andriani 2000) ; fish reproduct ion ( Nasut ion et al 2006) ; reproduct ion t est on
ex - sit u ( Said et al 2005) ; feeding habit s ( Jayadi et al 2013) ; infest at ions of ect oparasit es
( Am rullah et al 2013) ; analysis of fecundity and egg diam et er ( Kariyanti et al 2014) ; and
gonadal m at uration w it h live feed ( Jayadi et al 2015). How ever, lim it ed inform at ion is
available concerning t he dom estication of t he fish. The success of dom estication of M.
ladigesi is generally dependent on t he m aint enance of broodst ock, spaw ning or breeding
and rearing of larvae and j uvenile ( seed) in capt ivit y. The st udy aim ed t o det erm ine
fecundit y, hat ching rate of t he broodst ock and survival rat e of t he larvae and j uvenile of
M. ladigesi fed wit h different live feed.
M a t e r ial a n d Me t h od. The st udy w as conduct ed at t he freshw at er ornam ent al fish
hat chery at Manggala village, m unicipality of Makassar, sout h Sulaw esi, I ndonesia on
January t o July 2016.
Br oodst ock . Broodst ocks of M. ladigesi w ere collected from Bant im urung river and
Pat unung Asue River of Maros regency; Jennae River and Gow a Lorong River of
Pangkaj enne Kepulauan regency; Asanae River of Bone regency. The broodst ock w as
collected using a landing net wit h a m esh size of 1 m m , and t ransport ed t o t he hat chery
of freshw at er ornam ent al fish in Manggala, Makassar. Upon t he arrival, t he broodst ock
w as acclim atized and im m ersed in 2 m g L- 1 pot assium perm anganat e ( KMnO4 ) solution
for 10 m inut es.
Pr e pa r a t ion of w a t e r. Wat er sources w ere obt ained from t he ground w at er, w hich
pum ped int o 2 t anks. Before used, t he w ater was precipit at ed overnight, filtered, and
circulat ed t o broodst ock rearing, spaw ning, and larval rearing t anks by gravity.
Br oodst ock r e a r in g. The broodst ocks w ere m aint ained in a fiberglass t ank ( L x W x H;
200 x 150 x 75 cm ) , equipped wit h an aeration and filt ration syst em . The w at er volum e
in t he fiberglass t ank w as kept at 350 lit ers. Before st ocking, t he broodst ocks w ere
soaked in 1 m g L- 1 pot assium perm anganat e (KMnO4) for 10 m in. During t he rearing
periods, t he broodst ocks w ere fed t hree t ypes of live food; Daphnia sp., Chironom us sp.,
and Culex sp. I n t he first group, t he broodst ocks t hat w ere fed Daphnia sp., t he t ot al
lengt h of t he fem ale and m ale broodst ock w ere from 4.5 t o 5.4 cm and from 5.1 t o 6.3
cm respectively. I n t he second group, t he broodst ocks t hat w ere fed Chironom us sp., t he
t ot al lengt h of fem ale and m ale broodst ock w ere from 4.8 t o 5.6 cm , and fr om 5.0 t o 6.4
cm , respectively, w hile in t he t hird group, t hat w ere fed Culex sp., t he t ot al lengt h of t he
fem ale and m ale broodst ock w ere from 4.9 t o 5.5 cm and 4.9 t o 6.3 cm , respect ively.
Feed w as given t wice daily ad libit um . Fifty percent ( 50% ) of w at er exchange w as done
w eekly. Param et ers m easured w ere survival rat e, fecundity, and gonad m at urit y level.
The w at er qualit y param et ers observed w eekly w ere dissolved oxygen ( DO) , pH,
t em perat ure, and am m onia. Aft er 5 m ont hs of t he rearing period, 20 broodst ocks w ere
used for sam pling t o det erm ine fecundit y and gonad m at urity level of t he broodst ock.
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Spa w n in g. The broodst ocks w ere kept at a fiberglass t ank ( L x W x H; 130 x 80 x 60
cm ) , equipped wit h t he aeration system . The volum e of t he w at er in t he spaw ning t ank
w as 100 lit ers. The ratio of m ales t o fem ales w as 1: 2 ( Said & Mayasari 2007) . The
num ber fem ale t hat used w as 50 fem ales and 25 m ales. The feed w as given as
previously described in t he broodst ock rearing. The at t achm ent subst rate of t he fish eggs
w as m ade of t he r opes t hat st ret ched out t o resem ble t he plant root s. The subst rat e w as
placed in t he m iddle of t he t ank. Aft er 24 h, t he at t ached eggs w ere collected and
num bered. I ncubat ion t ank w as a plastic bucket filled wit h 10 liters of w ater. The
at t achm ent subst rat e of t he eggs w as incubat ed in a plastic bucket . Param eters
m easured w ere t he t ot al num ber of eggs; t he num ber of eggs hat ching; egg incubat ion
t im e; t he num ber of unhat ched eggs; and hat ching rat e. Aft er t he eggs hat ched int o
larvae, t hen t he larvae w ere t ransferred t o larval tanks.
La r va l r e a rin g. The larvae w ere m aint ained in a fiberglass t ank ( L x W x H; 60 x 40 x
35 cm ) , equipped wit h t he aerat ion system . The volum e of t he w at er in t he t ank w as 20
lit ers. Rearing of fish larvae was divided int o t hree groups: t he first group w as t he larvae
obt ained from t he broodst ock t hat fed Daphnia sp., t he second group w as t he larvae
generat ed from broodst ock t hat fed Culex sp., and t he t hird group w as t he larvae
obt ained from broodst ock t hat fed Chironom us sp. The num ber of larva used in each
group w as 200 individuals t hat w ere random ly dist ribut ed t o 4 t anks, and each t ank
consist ed of 50 larvae. Larval rearing w as carried out by spaw ning t im e at t he each
group. The feed used in each group w as sim ilar; nauplii of Daphnia sp. The larvae w ere
reared for 30 days. Feeding frequency w as t wice daily. Param et er m easured w as survival
rat e. Num ber of dead larvae w as calculat ed daily. Wat er qualit y m easured every w eek
such as dissolved oxygen, pH, t em perat ure, and am m onia.
Re su lt s a n d D iscu ssion
Br oodst ock r e a r in g. The survival rat es, fecundity and gonad m at urit y level of t he
broodst ocks t hat w ere fed t hree t ypes of live fish: Daphnia sp., larvae of Culex sp. and
Chironom us sp. are show n in Table 1. The survival rat e of t he broodst ock fed Daphnia sp.
w as t he highest , w hereas t he lowest w as observed in t he broodst ock feed larva Culex sp.
These result s w ere different wit h t he previous st udy of Jayadi & Husm a ( 2015) t hat
survival of t he broodst ocks t hat w ere fed Daphnia sp. w as 83.33% , w hile Chironom us sp.
and Culex sp. w ere 63.33% and 65.00% , respect ively.
Table 1
Survival rat es, fecundit y and gonadal m at urity level ( GML) of M. ladigesi fed Dapnia sp.,
larvae of Culex sp. and Chironom us sp. for 5 m ont hs
Treat m ent of feeding
Survival rat e ( % )
Fecundit y ( ind.)
Dapnia sp.
Chironom us sp.
Larva Culex sp.
91
86
81
65–281
49–172
37–154
Num ber ( ind.)
GML I I I
GML I V
4
16
9
11
8
12
Sim ilar t rend w as also observed in fecundit y, in which t he broodst ocks t hat w ere fed wit h
Daphnia sp. induced higher fecundit y com pared w it h ot her live feed. Fecundit y of M.
ladigesi t hat w ere obt ained from t his st udy show ed low er levels com pared wit h t hose in
t heir nat ural habit at as report ed by several researchers ( Andriani 2000; Nasut ion et al
2006; Karyant i et al 2014; Jayadi et al 2013) . The fecundit y of fish is affected by t he
lengt h, w eight , age, genetic fact ors, environm ental fact ors, food, species of fish ( Effendie
1979; Mondal & Kaviraj 2010; Bindu & Padm akum ar 2014) . Likew ise, t he num ber of
broodst ock t hat achieved t he highest gonadal m at urit y level ( GML) w as 16 in t he
broodst ock fed Daphnia sp., w hile t he broodst ock fed Chironom us sp. and Culex sp. w as
only 11 and 12 respect ively. The use of Dapnia sp., Chironom us sp. and larvae of Culex
sp. as live feed for M. ladigesi can im prove gonadal developm ent int o t he GML I I I and I V,
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because t he nut ritional value of feed given t hroughout t he rearing period ( Table 2) m et
t he dem and of t he broodst ock. The feed given to t he broodst ock had sim ilar proxim ate
analysis result s wit h M. ladigesi, in w hich t he prot ein cont ent w as 52.65% , fat w as
10.93% , and carbohydrat e w as 5.62% . Nut ritional value of t he feed given t o t he
broodst ock affect ed gonad developm ent and fecundit y ( Fernandez- Palacios et al 1995) .
During t he st udy, t he num ber of broodst ock t hat w ere used in each t reat m ent w as 100
individuals and reared for 5 m ont hs.
Table 2
The proxim at e analysis of t he live feed
Treat m ent of
feeding
Chironom us sp.
Dapnia sp.
Larva Culex sp.
Wat er
(% )
8.4
4.9
13.3
Ash
(% )
10.00
6.26
8.47
Prot ein
(% )
44.22
53.12
49.07
Fat
(% )
8.69
20.13
13.17
Carbohydrat e
(% )
28.69
15.59
15.99
The range of w at er qualit y during t he t he broodstock rearing of M. ladigesi is present ed in
Table 3. The range of w at er quality param et ers w ere w it hin t he lim its t hat can be
t olerat ed by M. ladigesi. The result s w ere sim ilar wit h t he previous st udy of Jayadi et al
( 2013) t hat investigat ed t he w at er qualit y param et ers of M. ladigesi in t heir nat ural
habit at s. The w at er qualit y param eters in t heir nat ural habit ats are as follow s:
t em perat ures ranged from 28- 30 o C; DO w as 5.8 t o 8.2 m g L- 1 ; pH ranged from 6.2 t o
8.2; NH3 w as < 0.008 m g L- 1 ; and nit rit e w as < 0.0003 m g L- 1
Table 3
The range of w at er qualit y during t he rearing of M. ladigesi broodst ock
Treat m ent of
feeding
Chironom us sp.
Dapnia sp.
Larva Culex sp.
Tem perat ure
( o C)
pH
DO ( m g L- 1 )
NH3 ( m g L- 1 )
Nit rit e ( m g L- 1 )
27.5–28.9
27.8–28.7
27.6–28.7
6.8–7.9
6.7–8.0
6.7–8.0
7.43–7.76
7.43–7.75
7.43–7.75
0.002–0.007
0.003–0.006
0.002–0.006
0.001–0.003
0.001–0.002
0.001–0.002
Spa w n in g. The results of M. ladigesi spaw ning obt ained on t he t ot al num ber of eggs;
num ber of hat ched eggs; num ber of unhat ched eggs; hat ching rat e and hat ching per iod are
depict ed in Tables 4, 5, and 6.
Table 4
Tot al num ber of eggs; num ber of hat ched eggs; num ber of unhat ched eggs; hat ching rat e and
hat ching per iod of M. ladigesi t hat were fed Daphnia sp.
Spawning
dat e
17 May 2016
19 May 2016
20 May 2016
21 May 2016
23 May 2016
24 May 2016
25 May 2016
27 May 2016
29 May 2016
Tot al
Average
Num ber of
eggs ( ind.)
121
84
96
129
86
107
83
75
68
849
94.33
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Hat ched
larvae ( ind.)
92
58
73
98
61
89
56
49
36
612
68
Num ber of unhat ched
eggs ( ind.)
29
26
23
31
25
18
27
26
32
237
26.33
1070
Hat ching
rat e ( % )
76.03
69.05
76.04
75.97
70.93
83.18
67.47
65.33
52.94
70.77
Hat ching
period ( days)
9
9
8
9
8
8
8
8
9
8.4
Table 5
Tot al num ber of eggs; num ber of hat ched eggs; num ber of unhat ched eggs; hat ching rat e and
hat ching per iod of M. ladigesi t hat were fed larva Culex sp.
Spawning
dat e
19 May 2016
20 May 2016
22 May 2016
24 May 2016
26 May 2016
28 May 2016
30 May 2016
Tot al
Average
Num ber of
eggs ( ind.)
112
76
106
83
73
62
53
565
80.71
Hat ched
larvae ( ind.)
75
51
79
57
46
39
28
375
53.57
Num ber of unhat ched
eggs ( ind.)
37
25
27
26
27
23
25
190
27.14
Hat ching
rat e ( % )
66.94
67.10
74.53
68.67
63.01
62.90
52.83
65.14
Hat ching
period ( days)
9
9
9
8
9
9
8
8.7
Table 6
Tot al num ber of eggs; num ber of hat ched eggs; num ber of unhat ched eggs; hat ching rat e and
hat ching per iod of M. ladigesi t hat were fed Chironom us sp.
Spawning
dat e
18 May 2016
19 May 2016
21 May 2016
23 May 2016
25 May 2016
26 May 2016
28 May 2016
30 May 2016
Tot al
Average
Num ber of
eggs ( ind.)
102
92
114
98
61
78
42
38
625
78.13
Hat ched
larvae ( ind.)
74
62
69
71
46
54
28
20
424
53
Num ber of unhat ched
eggs ( ind.)
28
30
45
27
15
24
14
18
201
25.13
Hat ching
rat e ( % )
72.55
67.39
60.52
72.45
75.40
69.23
66.67
52.63
67.10
Hat ching
period ( days)
8
8
9
9
9
8
9
9
8.6
M. ladigesi w as fed Dapnia sp. produced 849 eggs, wit h t he hat ching rat e of 70.77% ,
w hile t he num ber of eggs produced by t he broodst ock fed Chironom us sp. w as 625 eggs,
w it h t he hat ching rat e of 67.10% . M. ladigesi were fed larvae Culex sp. produced 565
eggs wit h t he hat ching rat e of 65.14% . The use of t he t hree t ypes of feed on M. ladigesi
caused different effect s on t he broodst ock ( Tables 4, 5 and 6) . The use of Daphnia sp.
result ed in bet t er result s t han larva of Cules sp. and Chironom us sp. Daphnia sp. have
high nut ritional values such as prot ein ( 53.12% ) and fat ( 20: 13% ) ( Table 2) w hich are
equal wit h t he body com position of M. ladigesi ( 52.65% prot ein, and 10.93% fat ) ( Jayadi
& Husm a 2015) . The qualit y of Pagrus m aj or eggs w as st rongly influenced by t he cont ent
of prot ein, fat , phosphorous, pigm ent s and essent ial fat t y acids of t he feed ( Wat anabe et
al 1984) . M. ladigesi eggs hat ched aft er 8- 9 days at t em perat ures of 27- 28 o C ( Tables 4,
5 and 6) . According t o Depeche & Billard ( 1994) t he lengt h of t he incubation tim e of fish
eggs depends on t he fish species and environm ent al fact ors such as t em perat ure, light
and oxygen. Based on t he result s of gonad m at urit y index of M. ladigesi, w e can conclude
t his fish m ay spaw n t hroughout t he year ( Jayadi et al 2016) . Spaw ning m odels of som e
fish species of t he genus Telm at herina have been report ed in several st udies such as T.
ant oniae ( Sum aset iadi 2003) ; T. celebensis ( Nasut ion 2004) ; T. bont i ( Jayadi et al
2006) . Fact ors t hat affect spaw ning in fish have been report ed by Scot t (1979) . M.
ladigesi m aint ained in captivity can spaw n aft er the availabilit y of spaw ning aggregation
sites. M. ladigesi is a kind of fish t hat at t ach t heir eggs t o t he subst rat e, such as
Clupeiform es ( Oht a 1984) ; Cypriniform es ( Long & Ballard 1976) ; Siluriform es
( Kobayakaw a 1985) .
La r va l r ea r in g. Wat er qualit y param et ers during larval rearing are show n in Table 7.
The w at er quality conditions w ere sim ilar t o t he fish nat ural habit at in t he wild ( Jayadi et
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al 2013) . Broodst ock of M. ladigesi t hat w ere fed Dapnia sp. spaw ned 9 tim es and
produced 612 t ot al num ber of larvae ( Table 8), while t he broodst ocks t hat w ere fed Culex
sp. spaw ned 7 tim es and generat ed 375 t ot al num ber of larvae ( Table 9) , and t he
broodst ocks fed Chironom us sp. spaw ned 8 t im es and produced 424 larvae ( Table 10) .
Table 7
The range of w at er qualit y during t he larval rearing of M. ladigesi
Group
Daphnia sp.
Larvae Culex sp.
Chironom us sp.
Tem perat ure ( o C)
27.9–29.0
27.8–29.0
27.9–29.1
pH
6.8–8.1
6.8–8.0
6.8–8.0
DO ( m g L- 1 )
7.64–7.78
7.63–7.77
7.63–7.78
NH3 ( m g L- 1 )
0.002–0.005
0.003–0.004
0.002–0.005
Survival rat e of larvae obt ained from t he broodst ock t hat w ere fed Daphnia sp. w as
39.02 % at age 5 day, 71.67% at age 10 days. The survival rat e of larvae at age 20 days
w as 78.18% , t he survival rat e at age 30 days w as 99.84 % ( Table 8) .
Table 8
Survival rat e of M. ladigesi larvae obt ained from the broodst ock t hat w ere fed Dapnia sp.
Dat e of
spawning
17
19
20
21
23
24
25
27
29
May 2016
May 2016
May 2016
May 2016
May 2016
May 2016
May 2016
May 2016
May 2016
Tot al
Average
Num ber of larvae
( ind.)
92
58
73
98
61
89
56
49
36
612
68
Survival rat e
at 5 days
(% )
33.37
29.78
34.76
39.78
40.32
38.06
42.78
49.52
42.79
Survival rat e
at 10 days
(% )
72.83
72.41
75.34
68.37
75.41
73.89
66.07
67.35
73.33
Survival rat e
at 20 days
(% )
81.56
75.26
75.05
78.57
75.45
80.81
76.21
77.35
83.33
Survival rat e
at 30 days
(% )
100
100
100
100
100
98.59
100
100
100
39.02
71.67
78.18
99.84
Survival rat e of larvae from t he broodst ocks t hat w ere fed larva of Culex sp. w as 38.53%
at age 5 days, 70.76% at age 10 days. The surv ival rat e of larvae at age 20 days w as
73.06% , t he survival rat e at age 30 days reached 96.92% ( Table 9) .
Table 9
Survival rat e of M. ladigesi larvae obt ained from t he broodst ocks t hat were fed lar vae Culex sp.
Dat e of
spawning
19
20
22
24
26
28
30
May 2016
May 2016
May 2016
May 2016
May 2016
May 2016
May 2016
Tot al
Average
Num ber of larvae
( ind.)
75
51
79
57
46
39
28
375
53.57
Survival rat e
at 5 days
(% )
30.67
39.71
32.67
42.69
40.78
35.79
47.42
Survival rat e
at 10 days
(% )
68.00
74.51
62.03
75.43
69.57
74.36
71.42
Survival rat e
at 20 days
(% )
70.23
74.51
69.38
77.27
70.57
75.07
74.42
Survival rat e
at 30 days
(% )
89.47
100
93.23
100
100
95.78
100
38.53
70.76
73.06
96.92
Survival rat e of larvae from t he broodst ocks t hat w ere fed Chironom us sp. w as 38.31%
at age 5 days, 62.44% at age 10 days, t he survival rat e of larvae at age 20 days w as
87.89% , t he survival rat e of larvae at t he age of 30 days reached 96.14% ( Table 10) .
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Table 10
Survival rat e of M. ladigesi larvae obt ained from t he broodst ocks t hat were fed Chironom us sp.
Dat e of
spawning
18
19
21
23
25
26
38
30
May 2016
May 2016
May 2016
May 2016
May 2016
May 2016
May 2016
May 2016
Tot al
Average
Num ber of larvae
( ind.)
74
62
69
71
46
54
28
20
424
53
Survival rat e
at 5 days
(% )
35.24
31.21
45.23
44.38
31.34
42.56
29.43
47.07
Survival rat e
at 10 days
(% )
59.62
60.74
55.21
56.23
65.22
69.37
62.57
70.55
Survival rat e
at 20 days
(% )
81.54
79.23
82.12
79.63
81.51
100
100
99.12
Survival rat e
at 30 days
(% )
92.35
97.32
89.23
98.74
91.45
100
100
100
38.31
62.44
87.89
96.14
The fish larvae abilities t o t ake food from out side det erm ine t he survival and subsequent
developm ent of t he fish. Fish larvae st art ed t o consum e food aft er t he larvae can open
it s m out h ( Hunt er 1981; Bagarinao 1986; Blaxt er 1988) . The result s of t his st udy
show ed t hat t he larvae of M. ladigesi st art ed t o open t he m out h at 70- 72 hours aft er
hat ching and t aking food from t he out side before t he endogenous w ere absorbed.
Several types of fish t ook food before t he egg yolk run out as show n in Oxyeleot ris
m arm orat a ( Wahyuningrum 1991) ; Myst us nem ur us ( Am or nsakun & Hasan 1997) ; Lat es
calcarifer ( Kohno et al 1986) ; and several species of grouper such as Epinephelus
fuscogut t at us ( Kohno et al 1990) ; E. m alabaricus ( Ruangpanit et al 1993) ; E. t auvina
( Husain & Higuchi 1980) and E. m icrodon ( Jayadi & Ardiansyah 2012) . Fish larvae t ook
food from t he out side, w hich depended on t he t ype and am ount of food available ( Hunt er
1980) . Food select ed by t he larvae w as influenced by t he abundance, size, agility, and
t he feasibility or easy invisible of t he food by t he larvae ( Noakes & Gordin 1988) . The
fish larvae can t ake t he food t hat t hey can see in t he w at er ( Hunt er 1981) .
As show n in Tables 8, 9 and 10, t he high m ort ality of larvae occurred at ages 1 t o
10 days aft er hat ching, t he feeding period from endogenous t o exogenous. This period is
a critical period of fish larvae ( I w ai 1972; Bagarino 1986; Fukuhara 1988) . Wit h t he
availabilit y of suit able food in t he t ransition, the larval m ort alit y could be reduced
( Noakes & Gordin 1988) . M. ladigesi larvae is able t o eat live food such as nauplius of
Daphnia sp. ( size < 0.08 m m ) . Som e st udies report ed t hat alm ost all t ypes of fish larvae
ut ilize plankt on for early feeding because t he plankt on fulfill t he size, com position,
m ovem ent and digestion capacit y of larvae ( Watanabe et al 1983; Ahlgren et al 1990;
Holt 1992; Arief et al 2009) . Selection of t he t ype of live feed for fish larvae is
recom m ended by som e researchers for several reasons. Live food is easily digest ed by
t he larvae because t he live food cont ains digestive enzym es. This can be seen from t he
increased activit y of prot ease enzym es in t he digest ive t ract of w hitefish w ere fed nat ural
rot ifer ( St roband & Dabrow ski 1979) . The use of live feed in roach fish result ed in a
higher activit y of t he enzym e t rypsin ( Hofer 1985) . The second reason, because t he
nut ritional value of nat ural feed is alm ost sim ilar wit h t he fish's body ( St roband &
Dabrow ski 1979) , so t he nut rit ional needs of t he fish can be fulfilled from of live feed.
The t hird reason is live feed does not quickly decom pose, so it does not pollute t he
environm ent . Thus w ater quality param et ers w ere st ill kept in a good condition.
Con clusion s. The use of live feed affect ed t he successfulness of rearing and spaw ning of
t he broodst ock, and t he larval rearing of M. ladigesi. Live feed such as Daphnia sp.,
Culex sp. and Chironom us sp. are suit able for t he broodst ock. The incubation period w as
8- 9 days, w hereas t he hat ching rat e w as 65.14- 70.77% . Larvae of M. ladigesi st art ed t o
open t he m out h at 70- 72 hours aft er hat ching and t ook food fr om t he out side before t he
endogenous w ere exhaust ed. The size of t he nauplius of Daphnia sp. given t o t he larvae
w as < 0.08 m m . The survival rate of larvae w as 38.31- 39.02% unt il age 5 days, 62.44-
AACL Bioflux , 2016, Volum e 9, I ssue 5.
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1073
71.67% at 10 days, 20- 30 days aft er hat ching t he survival rat e reached ranged from
73.06- 99.84% .
Ack n ow le dge m e n t s. The aut hors w ould like t o t hank DP2M DI KTI I ndonesia for t he
research funding t hrough SKI M com pet itive research grant s in 2016. We also t hank
Muham m ad Raj im an Hasbi for t he use of freshw at er ornam ent al fish hat chery at
Manggala village, m unicipalit y of Makassar.
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Received: 24 August 2016. Accept ed: 30 Sept em ber 2016. Published online: 16 Oct ober 2016.
Aut hor s:
Jayadi Jayadi, Depar t m ent of Aquacult ur e, Facult y of Fisher y and Mar ine Scince, I ndonesia Muslim Univer sit y,
Jl. Ur ip Sum ohar j o Km 05, Makassar 90231, I ndonesia, e- m ail: j ayadi_fat r ial@yahoo.com
Am r ah Husm a, Depar t m ent of Aquacult ur e, Facult y of Fisher y and Mar ine Scince, I ndonesia Muslim Univer sit y,
Jl. Ur ip Sum ohar j o Km 05, Makassar 90231, I ndonesia, e- m ail: am r ah_husm ah64@gm ail.com
Nur sahr an, Depar t m ent of Aquacult ur e, College of Mar ine Sciences and Fisher ies, BALI KDI WA, Jl. Ur ip
Sum ohar j o Km 11, Makassar 90231, I ndonesia, e- m ail: nur syahr an00@gm ail.com
Ar diansyah, Depar t m ent of Aquacult ur e, Agr icult ur al Polyt echnic of Pangkep, Pangkaj enne and Kepulauan, Jl.
Por os Makassar - Par e- Par e Km 83 Mandalle, Pangkep Sulawesi Selat an 90655, I ndonesia, e- m ail:
ar di_kism an@yahoo.com
Sr iwahidah, Depar t m ent of Aquacult ur e, Agr icult ur al Polyt echnic of Pangkep, Pangkaj enne and Kepulauan, Jl.
Por os Makassar - Par e- Par e Km 83 Mandalle, Pangkep Sulawesi Selat an 90655, I ndonesia, e- m ail:
sr iwahidah@gm ail.com
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How t o cit e t his ar t icle:
Jayadi J., Husm a A., Nursahr an, Ar diansyah, Sr iwahidah, 2016 Dom est icat ion of Celebes r ainbow fish
( Mar osat her ina ladigesi) . AACL Bioflux 9( 5) : 1067- 1077.
AACL Bioflux , 2016, Volum e 9, I ssue 5.
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