The occurrence of yellow catfish
Microsatellites are a useful tool for genetic analyses because of their abundance across genomes and the high level of polymorphism (Tautz & Renz 1984). In recent years, microsatellites have been widely used in aquaculture to analyze the genetic variation, to construct linkage maps, to map the quantitative traits loci and to perform genetic identification (DeWoody & Avise 2000). Previous studies isolated several polymorphic microsatellite makers of yellow catfish, which were then applied to investigate genetic structure of populations from the upper and middle reaches of the Yangtze River and other river basins in China (Ma et al. 2006; Liu et al. 2008; Li et al. 2009; Wu et al. 2010). However, the spawning grounds of yellow catfish are located mainly in lakes. Many lakes distributed in the middle and lower reaches of the Yangtze River form a group of shallow lakes, unique in the world. So far, there has been no report on the genetic diversity and population structure of yellow catfish from the middle and lower reaches of the Yangtze River.
In this study, we selected thirteen available microsatellite markers from the existing literature (Liu et al. 2008; Li et al. 2009; Wu et al. 2010) and genotyped five yellow catfish populations sampled from lakes in the middle and lower reaches of the Yangtze River. The objectives of the present study were as follows: (1) to fully understand the genetic diversity and population structure of yellow catfish in five lakes; (2) to gather genetic data to help artificial propagation programs, effective conservation and management of yellow catfish.
Yellow catfish specimens were collected from five lakes in the middle and lower reaches of the Yangtze River, China, including Poyang Lake (PY) in the middle reaches, Caohu Lake (CH), Gehu Lake (GH), Hongze Lake (HZ) and Taihu Lake (TH) in the lower reaches (Fig. 1). Twenty five individuals were randomly sampled from each population. A caudal fin clip from each specimen was taken and stored in 95% ethanol for DNA extraction.
Total genomic DNA was extracted from the tail fin using the Ezup Column Animal Genomic DNA Kit (Sangon, Shanghai) following the manufacturer’s protocol. Quantity and quality of the extracted DNA were estimated on 1% agarose gels stained with ethidium bromide (EB). Thirteen specific microsatellite loci of yellow catfish (Table 1) were amplified by PCR on a Mastercycler gradient apparatus (Eppendorf).
Information of the thirteen microsatellite loci analyzed in five populations of yellow catfish Motif – sequences inside parenthesis indicate the motif sequence of the microsatellite DNA and subscripted numbers indicate the number of repeats ; Temp. – annealing temperature for PCR
Locus
Motif
Primer sequence (5′–3′)
Temp. (°C)
Expected size (bp)
Number of alleles
Reference
AG12
(GA)6A(AG)26
F: TTCTGAGGGGATGGTG R: GCGGTGCTCTGTGGTTGTC
60
228–335
5
Wu et al. 2010
AG48
(AG)13GGT(GA)5GC(GA )9
F:GCTGATACATTCTTTATTAGGGCACC R: GTCGCACTTCCCCTCTGTCA
57
185–451
6
AG128
(AG)23
F: AAACCGACGGGACAAAAGAT R: CTCTGCCTCACTAACT
51
91–145
9
CT30
(CT)9T(TC)2TT(TC)21
F: ACACCAAAACATTGTGCTAC R: ATTCAGGAGATCCCGACACT
55
237–298
4
CT42
(TC)6
F: GCAGAGGGTTGCTTTTGCCTTTTA R: CAACAATCACATTCTATGAGGAGT
55
125–150
3
CT81
(CT)6G(TC)4TG( TC)8
F: GTCTCCATCACTGCCACAT R: TCAGCAATTATGTGAAAAGTGTCT
55
126–176
5
HLJYC13
(CA)23
F:GACCCAGTTCCCACATTG R:GGCTACCACATCCCTCAT
58
179–207
4
Li et al. 2009
HLJYC17
(TC)25
F:ATGGTATAAACATGGTGCTA R:ATGATGCTGATAGGGTGA
58
170–188
3
HLJYC31
(CA)26
F:CAGGATGGAGGTGTAAAG R:ATAAAGCTGTGATGTGCC
55
285–317
4
HLJYC45
(TG)29
F:TGGGTCTCTCTGGGTTCA R:GCGGCTTCACTCACTTCC
56
278–312
3
HLJYC60
(CA)28(TTTG)7
F:GATCAACGTCCAACAGAG R:GGAAAGAAAGATGGCTAG
56
250–282
4
HLJYC66
(TG)27
F:ACACTGACATACACTGGCATAA R:CTGGCAACGTGTTTCTGGCATAA
56
243–295
4
HSY105
(CTAT)14
F:ACTCACGTTGTCAGTTTATCAC R:ACACAAGAAATCCCCTCG
53
150–172
4
Liu et al. 2008
PCR was conducted in a reaction mixture of 20 μl containing 1 μl genomic DNA (50 ng pl-1), 2μl of 10 × PCR buffer [40 mmol KCl, 8 mmol Tris-HCl (pH 8.8), 120 nmolKCl, 1.2 mmol MgCl2], 400 nmol each of reverse and forward primers, 0.5 U Taq DNA polymerase. The PCR amplification conditions used herein were as follows: initially denatured at 94°C for 5 min followed by 30 cycles (denaturation at 94°C for 30 sec, annealing at 51–60°C for 30 sec, and extension at 72°C for 1 min), with a final extension for 10 min at 72°C. Electrophoresis was conducted in 1.4% agarose gel to confirm successful DNA amplification.
The PCR products were run on 8% polyacrylamide gels in 0.5 × TBE buffer for 2–3 hours. After electrophoresis, the gels were silver stained and photographs were taken using a Nikon Coolpix 4500 digital camera. The 25 bp DNA Ladder (Invitrogen, USA) was used to determine the allele size. Each sample was screened 2–3 times for each primer in order to reduce allele misscoring.
The expected heterozygosity corrected for sampling bias, the observed heterozygosity (
The MEGA 6.0 software package (Tamura et al. 2013) was used to construct an UPGMA tree of relationships between the populations. Bayesian clustering analysis implemented with Structure 2.3.4 (Pritchard et al. 2000) was performed to estimate the most likely number of genetic clusters (K) of populations and assign individuals to those clusters without prior information on the origin of samples. The admixture model was employed, with 20 000 burn-in periods and 1 000 000 Markov-chain Monte Carlo (MCMC) iterations based on the discriminating loci. To identify the most likely posterior probability K value, the simulation program was run with increasing numbers of clusters (K) from two to five, and a plateau was used to indicate the most likely K (Falush et al. 2007). For each successive value of K, the inferred clusters were analyzed and visualized as colored box plots using the Distruct program (Rosenberg 2004).
For the 125 individuals from the five populations, a total of 58 alleles were identified across 13 microsatellite loci ranging from 90 to 450 bp. The average number of alleles per locus was 4.4, ranging from 3 (loci CT42, HLJYC31 and HSY105) to 9 (loci AG128). The observed heterozygosity (
Polymorphic information at 13 microsatellite loci of five populations of yellow catfish Ae – Effective allelic number; HO – observed heterozygosity; HE – expected heterozygosity; PIC – polymorphic information content; FIS – inbreeding coefficient
Locus
CH
GH
HZ
PY
TH
Overall
Ae
PIC
Ae
PIC
Ae
PIC
Ae
PIC
Ae
PIC
Ae
PIC
AG 12
2.81
0.52
0.66
0.58
0.193
4.24
0.68
0.78
0.72
0.110
3.24
0.72
0.71
0.64
-0.041
4.50
0.68
0.79
0.74
0.126
3.98
0.68
0.76
0.71
0.092
4.07
0.66
0.76
0.68
0.096
AG48
4.39
0.60
0.79
0.74
0.223
4.05
0.68
0.77
0.71
0.097
4.18
0.92
0.78
0.72
-0.209
3.38
0.64
0.72
0.65
0.091
3.64
0.48
0.74
0.68
0.339
4.61
0.66
0.79
0.70
0.106
AG128
5.43
0.84
0.83
0.79
-0.029
7.10
0.84
0.88
0.84
0.022
6.10
0.56
0.85
0.82
0.330
5.00
0.84
0.82
0.77
-0.050
5.81
0.84
0.84
0.81
-0.015
6.48
0.78
0.85
0.81
0.053
CT30
3.69
0.44
0.74
0.67
0.396
2.51
0.32
0.61
0.52
0.468
3.56
0.64
0.73
0.67
0.110
2.80
0.34
0.66
0.59
0.503
2.89
0.60
0.67
0.60
0.082
3.59
0.46
0.72
0.61
0.307
CT42
1.22
0.20
0.19
0.18
-0.082
1.08
0.08
0.08
0.08
-0.031
1.04
0.04
0.04
0.04
-0.020
1.00
0.00
0.00
0.00
NA
1.08
0.08
0.08
0.08
-0.031
1.08
0..08
0.08
0.08
-0.055
CT81
1.47
0.28
0.32
0.31
0.123
1.51
0.36
0.34
0.31
-0.061
1.18
0.16
0.15
0.08
-0.070
1.33
0.28
0.26
0.24
-0.118
1.28
0.24
0.23
0.21
-0.087
1.35
0.26
0.26
0.23
-0.032
HLJYC13
3.62
0.72
0.74
0.67
0.006
3.23
0.56
0.70
0.63
0.189
3.37
0.60
0.72
0.65
0.147
1.79
0.44
0.45
0.37
0.004
3.62
0.56
0.74
0.67
0.227
3.57
0.58
0.72
0.60
0.123
HLJYC17
2.57
0.40
0.62
0.53
0.345
3.06
0.44
0.69
0.61
0.346
3.54
0.76
0.73
0.67
-0.059
2.68
0.48
0.64
0.55
0.235
3.10
0.56
0.70
0.63
0.185
3.59
0.53
0.72
0.60
0.204
HLJYC31
2.59
0.36
0.63
0.54
0.414
2.83
0.44
0.66
0.57
0.320
2.93
0.36
0.67
0.59
0.454
2.96
0.28
0.68
0.59
0.577
2.83
0.40
0.66
0.57
0.382
2.96
0.37
0.66
0.57
0.430
HLJYC45
2.94
0.76
0.67
0.56
-0.152
2.88
0.68
0.67
0.59
-0.042
3.34
0.52
0.72
0.64
0.258
3.16
0.64
0.70
0.63
0.064
3.73
0.60
0.75
0.68
0.180
3.39
0.64
0.71
0.62
0.067
HLJYC60
3.82
0.60
0.75
0.69
0.187
3.04
0.44
0.68
0.62
0.345
3.45
0.56
0.72
0.65
0.212
3.10
0.64
0.69
0.63
0.056
3.01
0.56
0.68
0.60
0.162
3.43
0.56
0.71
0.64
0.192
HLJYC66
2.75
0.44
0.65
0.58
0.308
3.71
0.24
0.75
0.68
0.671
2.92
0.28
0.67
0.61
0.575
1.22
0.16
0.19
0.18
0.138
3.05
0.44
0.69
0.61
0.345
3.03
0.31
0.67
0.53
0.459
HSY105
1.44
0.20
0.31
0.28
0.347
1.45
0.20
0.32
0.28
0.354
1.18
0.12
0.15
0.14
0.202
1.04
0.04
0.04
0.04
-0.020
1.28
0.12
0.22
0.21
0.449
1.27
0.14
0.21
0.19
0.335
Average
2.98
0.49
0.61
0.55
0.180
3.13
0.46
0.61
0.55
0.233
3.08
0.48
0.59
0.53
0.168
2.61
0.42
0.51
0.46
0.162
3.03
0.47
0.60
0.54
0.190
3.26
0.46
0.60
0.53
0.187
Diversity measures for each population showed that the mean number of alleles per locus was very similar in each population. The GH and HZ populations were the most diverse populations having the highest allelic richness, 3.13 and 3.08 respectively, while the PY population – the lowest one (2.61). The observed heterozygosity (
Of the 65 population-locus cases, 42 (64.6%) were in HWE (
Locus
Test in each population
Multi-population test
CH
GH
HZ
PY
TH
AG12
0.000
0.808
0.009
0.015
0.028
0.015
AG48
1.000
0.386
0.386
0.060
0.072
0.465
AG128
0.543
0.645
0.345
0.345
0.004
0.345
CT30
0.000
0.033
0.018
0.100
0.095
0.000
CT42
0.970
0.999
1.000
1.000
0.999
0.978
CT81
0.877
0.805
0.987
0.906
1.000
0.999
HLJYC13
0.840
0.114
0.213
0.989
0.044
0.115
HLJYC17
0.015
0.042
0.003
0.000
0.032
0.067
HLJYC31
0.118
0.003
0.089
0.061
0.095
0.114
HLJYC45
0.089
0.028
0.011
1.000
0.005
0.034
HLJYC60
0.027
0.065
0.083
0.299
0.156
0.318
HLJYC66
0.252
0.089
0.384
0.275
0.198
0.987
HSY105
0.001
0.123
0.015
0.015
0.022
0.009
multi-locus test
0.387
0.957
0.215
1.000
1.000
1.000
The pairwise
Pairwise
Population
CH
GH
HZ
PY
TH
CH
∗∗∗
0.0302
0.0275
0.0810
0.0471
GH
0.0806
∗∗∗
0.0170
0.0642
0.0258
HZ
0.0722
0.0551
∗∗∗
0.0852
0.0169
PY
0.1377
0.1107
0.1409
∗∗∗
0.0746
TH
0.1077
0.0712
0.0541
0.1253
∗∗∗
AMOVA analysis of five populations of yellow catfish
Source of variation
d.f.
Sum of squares
Variance components
Percentage of variation
Fixation index
One group
Among populations
4
52.276
0.18565 Va
4.67
< 0.001
Within populations
245
927.680
3.78645 Vb
95.33
Among groups
1
23.946
0.18128 Va
4.44
< 0.001
Among populations within groups
3
28.330
0.11314 Vb
2.77
Within populations
245
927.680
3.78645 Vc
92.79
A UPGMA dendrogram of the five populations based on genetic distance estimates is shown in Fig. 2. The PY population from the lake located in the middle reaches of the Yangtze River separated as an independent branch and the other four populations from the lakes in the lower reaches of the Yangtze River clustered together as a separate branch. Bayesian clustering suggested the presence of two groups (K = 2) as the most likely, although most individuals showed mixed ancestry. There was a relatively little admixture exhibited by the PY population. The Bayesian clusters were similar to those revealed by UPGMA typology (Fig. 3).
Most of the microsatellite loci analyzed in this study were highly informative (PIC > 0.5, Botstein et al. 1980). The overall number of effective alleles per locus and the expected heterozygosity were consistent with the comprehensive research of DeWoody & Avise 2000 on microsatellite variation in freshwater fish (AE = 7.5 and
The comparison of the expected and observed heterozygotes indicated the heterozygote deficit in all populations. A similar phenomenon was also observed in the previous analysis of other closely related bagrid species (Powell 2012). Furthermore, positive moderate
The
To preserve the wild sources in China, hatchery-produced juveniles have been released annually into the lower reaches of the Yangtze River over the last two decades. However, many of these practices have been undertaken without a thorough understanding of the genetic background (Chen et al. 2012). The effective size of wild populations could be reduced through introductions of large numbers of hatchery-reared juveniles that have lower levels of genetic variation (Ryman & Laikre 1991). Large releases of sea urchins (
In conclusion, thirteen microsatellite loci revealed a moderate level of genetic diversity of the five yellow catfish populations from the middle and lower reaches of the Yangtze River. A moderate genetic differentiation was determined between the middle and lower groups, while low genetic differentiations were found within the lower populations. In situ conservation strategies should be preferred, and artificial propagation should also be adopted to enlarge the population size.