isolation and characterisation of microsatellite loci in the tire track eel, mastacembelus favus and...
TRANSCRIPT
MICROSATELLITE LETTERS
Isolation and characterisation of microsatellite loci in the tiretrack eel, Mastacembelus favus and cross-species amplification
Amirul Firdaus Jamaluddin Jamsari •
So Nam • Bui Minh Tam • Mohd Nor Siti-Azizah
Received: 25 November 2013 / Accepted: 25 December 2013 / Published online: 31 December 2013
� Springer Science+Business Media Dordrecht 2013
Abstract Nine microsatellite loci were isolated and
characterized in the tire track eel, Mastacembelus favus by
using library enriched for microsatellite region. Among 47
specimens collected from Mekong River, the number of
alleles ranged from 2 to 17 while levels of observed and
expected heterozygosities ranged from 0.021 to 0.873 and
from 0.021 to 0.893, respectively. The primers were suc-
cessfully tested in six closely related species, hence valu-
able for investigating population genetics and other related
aspects of M. favus and its congener species.
Keywords Mastacembelus favus � Enriched library �Microsatellites � Cross-amplification � Conservation
The tire track eel, Mastacembelus favus (Mastacembelidae)
is a widely distributed tropical freshwater fish across
Thailand, Lao PDR, Cambodia, Vietnam and Peninsular
Malaysia. It is considered as an excellent food fish and
sometimes seen in the aquarium trade (Jamsari pers. obs.;
Froese and Pauly 2013). In contrast to its significant value,
information on its basic ecology and biology i.e. migratory
pattern, spatial and temporal patterns of population
dynamics and evolutionary trends is still scarce or
unknown. Therefore, to aid the monitoring of the species,
development of novel microsatellites from M. favus and
cross-amplification of six congeners were conducted.
Genomic DNA was extracted from a single individual of
M. favus using AquaGenomic DNA isolation Kit (Bio-
Syntech) and microsatellite-enriched library protocol as
described in Jamsari et al. (2011). Fifty-one positive col-
onies were selected for sequencing. However, only 17
sequences exhibited good signal data with at least eight
repeat microsatellite motifs and primers were designed
using Primer3 (Untergasser et al. 2007). Preliminary
assessment on several individuals of M. favus with opti-
misation of annealing temperatures (40–65 �C) indicated
only nine loci with successful amplifications. These were
subsequently labelled with fluorescent dye for multiplex
PCR (Table 1).
Forty-seven individuals of M. favus collected from
Mekong River were then assayed for the nine microsatellite
characterisation. The loci were arranged in two 25 ll
multiplex PCR amplifications and unless otherwise stated,
PCR protocol was as described in Mytaq Red DNA poly-
merase (Bioline) standard protocol. Allelic data was ana-
lyzed using PeakScanner v1.0 software (Applied
Biosystems) with GS500 (Applied Biosystems) as the
internal size standard.
Results generated from Arlequin version 3.1 (Excoffier
et al. 2005) showed that the number of alleles per locus for
polymorphic loci ranged from 2 to 17 with a mean of 7.4.
The observed and expected heterozygosities ranged from
0.021 to 0.873 and from 0.021 to 0.893, respectively. All
A. F. J. Jamsari (&) � M. N. Siti-Azizah
School of Biological Sciences, Universiti Sains Malaysia,
11800 Penang, Malaysia
e-mail: [email protected]
S. Nam
Inland Fisheries Research and Development Institute (IFReDI),
Fisheries Administration, 186, Norodom Blvd., Phnom Penh,
Cambodia
B. M. Tam
College of Aquaculture and Fisheries, Can Tho University,
Can Tho, Vietnam
M. N. Siti-Azizah
Centre for Marine and Coastal Studies (CEMACS-Muka Head),
Universiti Sains Malaysia, 11800 Penang, Malaysia
123
Conservation Genet Resour (2014) 6:477–479
DOI 10.1007/s12686-013-0132-1
Ta
ble
1C
har
acte
riza
tio
no
fn
ine
mic
rosa
tell
ites
for
47
ind
ivid
ual
so
fti
retr
ack
eel,
Ma
sta
cem
bel
us
favu
sco
llec
ted
fro
mM
eko
ng
Riv
er
Lo
cus
Pri
mer
seq
uen
ce(50 –
30 )
Mu
ltip
lex
set
Rep
eat
mo
tif
Gen
Ban
kac
cess
ion
no
.A
llel
esi
ze(b
p)
Ta
(�C
)M
eko
ng
Riv
er
(n:4
7)
NA
HO
HE
P
MF
01
-E0
7F
:GG
GT
CC
AC
GA
GT
GT
TC
AA
AT
1(T
G) 1
1K
F8
00
88
01
92
–1
98
40
–5
55
0.5
96
0.6
11
0.1
61
8
R:H
EX
-CA
AG
GG
CT
CT
CC
AG
TG
TC
AT
MF
01
-D0
7F
:HE
X-C
AC
CA
GC
AA
CC
TG
CA
TT
TT
T1
(CA
) 22
KF
80
08
81
11
9–
15
14
5–
55
11
0.7
45
0.8
48
0.0
93
3
R:A
TG
TA
TG
CA
GC
CT
GG
AC
CT
T
MF
03
-P1
0F
:FA
M-T
GA
CC
AG
AG
GT
CA
AG
CA
GA
A1
(CA
) 11
KF
80
08
82
24
9–
25
95
0–
60
20
.02
10
.02
11
.00
00
R:C
CG
TC
CT
CC
AC
AG
GT
AG
AC
A
MF
02
-P0
4F
:GT
GG
AC
TA
AC
AG
AG
GC
AT
TC
G1
(CA
) 26
KF
80
08
83
27
3–
32
74
0–
50
17
0.8
73
0.8
93
0.2
82
3
R:H
EX
-CG
TG
GA
CT
AG
GT
GA
CG
TG
AA
MF
01
-H0
5F
:HE
X-C
GG
TG
AA
GA
CA
CT
CG
CA
TA
A2
(CA
) 17
KF
80
08
84
10
1–
13
04
0–
55
10
0.7
45
0.7
75
0.6
29
3
R:A
CT
TC
CT
CC
AC
CT
CC
GT
TT
T
MF
01
-F0
6F
:FA
M-C
GG
CT
GA
AT
GT
TA
CC
AC
TT
G2
(CA
) 10
KF
80
08
85
14
1–
14
54
0–
55
30
.51
10
.45
40
.78
66
R:C
AT
TC
GC
AG
TA
AA
AC
GC
AG
A
MF
01
-A0
6F
:GG
CC
TC
TT
CT
GA
CA
CT
CT
GC
2(C
A) 1
5K
F8
00
88
61
89
–1
99
40
–5
06
0.6
38
0.6
26
0.7
49
4
R:H
EX
-CC
AC
AG
GA
CA
TG
GA
CC
TT
CT
MF
01
-B0
7F
:HE
X-C
GA
TG
AA
GA
GG
AG
GC
TT
GA
C2
(TG
) 8A
GK
F8
00
88
72
77
–3
14
40
–5
57
0.7
02
0.6
41
0.9
75
9
R:C
CT
CC
AC
TC
TG
GT
CG
AT
GT
T(T
G) 1
0
MF
02
-P0
8F
:FA
M-C
CA
CA
GA
AA
CT
TC
CC
CT
GA
A2
(CA
) 9A
AK
F8
00
88
82
02
–2
16
40
–5
56
0.6
81
0.6
93
0.6
43
2
R:T
GT
GG
GT
TG
AT
GT
AG
GC
TG
A(C
A) 4
All
ele
size
ran
ge
inb
ase
pai
rs(b
p);
ann
eali
ng
tem
per
atu
re(T
a);
nu
mb
ero
fal
lele
s(N
A);
ob
serv
edh
eter
ozy
go
sity
(HO
);ex
pec
ted
het
ero
zyg
osi
ty(H
E);
Pv
alu
e(P
)
478 Conservation Genet Resour (2014) 6:477–479
123
loci conformed to Hardy–Weinberg equilibrium with no
evidence of linkage disequilibrium. Analysis using Mi-
croChecker v2.2.3 (Van Oosterhout et al. 2004) indicated
no evidence for null alleles, large allele dropout, and
scoring error due to stuttering. The potential of cross-
amplification was also tested for six Asian Mastacembelus
species. Relatively high level of cross-species amplification
was observed ranging from 4 to 8 loci (Table 2).
Overall, high variable microsatellite markers developed
in this study would be useful in assessing the patterns of
population genetic structure, genetic diversity, history
biogeography, breeding strategy, fishery management and
formulating conservation priorities of this and closely
related species.
Acknowledgments We would like to acknowledge Universiti Sains
Malaysia for research funding (Research University Grant—1001/
PBIOLOGI/815061) and for Vice Chancellor’s Award to the first
author for his Ph.D. program. We would like to thank Phanara Thach,
Nguyen Hong Quyet Thang and Dang Quang Hieu for their assistance
in collecting the samples.
References
Excoffier L, Laval G, Schneider S (2005) ARLEQUIN (v. 3.11): an
integrated software package for population genetics data
analysis. Evol Bioinform Online 1:47–50
Froese R, Pauly D (eds) (2013) FishBase. World Wide Web electronic
publication. http://www.fishbase.org, version (10/2013). Acces-
sed 4 October 2013
Jamsari AFJ, Min Pau T, Siti Azizah MN (2011) Isolation and
multiplex genotyping of polymorphic microsatellite DNA
markers in the snakehead murrel, Channa striata. Genet Mol
Biol 34:345–347
Untergasser A, Nijveen H, Rao X, Bisseling T, Geurts R, Leunissen
JA (2007) Primer3Plus, an enhanced web interface to Primer3.
Nucleic Acids Res 35(Web Server issue):W71–W74
Van Oosterhout C, Hutchinson WF, Wills DPM, Shipley P (2004)
Micro-checker: software for identifying and correcting genotyp-
ing errors in microsatellite data. Mol Ecol Notes 4:535–538
Ta
ble
2C
ross
amp
lifi
cati
on
resu
lts
for
six
spec
ies
of
mas
tace
mb
elid
s
Sp
ecie
sL
ocu
s
MF
01
-E0
7M
F0
1-D
07
MF
03
-P1
0M
F2
-P0
4M
F0
1-H
05
MF
01
-F0
6M
F0
1-A
06
MF
01
-B0
7M
F2
-P0
8
Ma
sta
cem
bel
us
arm
atu
s?
-?
-?
??
??
Ma
sta
cem
bel
us
alb
og
utt
atu
s-
DB
?W
A?
?W
AW
A?
Ma
sta
cem
bel
us
no
top
hth
alm
us
??
?D
B?
??
??
Ma
sta
cem
bel
us
un
ico
lor
-?
??
?-
??
?
Ma
sta
cem
bel
us
eryt
hro
taen
ia-
??
??
??
??
Ma
sta
cem
bel
us
tin
win
i?
WA
??
??
?D
B?
Su
cces
sfu
lam
pli
fica
tio
n(?
);w
eak
amp
lifi
cati
on
(WA
);d
ou
ble
ban
dam
pli
fica
tio
n(D
B);
no
amp
lifi
cati
on
(-)
Conservation Genet Resour (2014) 6:477–479 479
123