Submit or Track your Manuscript LOG-IN

Temporal Variation of Biometric Indices for Megalaspis cordyla (Linnaeus, 1758) from the Bay of Bengal, Bangladesh

SJA_38_5_300-310

Research Article

Temporal Variation of Biometric Indices for Megalaspis cordyla (Linnaeus, 1758) from the Bay of Bengal, Bangladesh

Most. Shakila Sarmin1,2, Md. Ashekur Rahman1,2, Most. Farida Parvin2,3, Mst. Shefaly Khatun4, Kazi Ahsan Habib5, Wasim Sabbir6, Jun Ohtomi7 and Md. Yeamin Hossain1*

1Department of Fisheries, University of Rajshahi, Rajshahi- 6205, Bangladesh; 2Institute of Natural Resources Research and Development, Rajshahi-6206, Bangladesh; 3Institute of Environmental Science (IES), University of Rajshahi, Rajshahi- 6205, Bangladesh; 4Department of Zoology, Rajshahi College, National University, Bangladesh; 5Department of Fisheries Biology and Genetics, Sher-e-Bangla Agricultural University, Bangladesh; 6Fisheries and Marine Resource Technology Discipline, Khulna University, Khulna, Bangladesh; 7Faculty of Fisheries, Kagoshima University, 45020 Shimoarata, Kagoshima 890-0056, Japan.

Abstract | This study described the population sizes structure, growth pattern, maturity size (Lm), and optimum catchable size (Lopt) of Megalaspis cordyla. Fish were sampled (male = 720, female = 793) from commercial vessels operating in the Bay of Bengal (BoB), Bangladesh between January-December 2020. All lengths (TL, total; FL, fork; SL, standard length), were taken using a fish measuring board to 0.01 cm as well as a digital balance is used to weigh body weight (BW) to 0.01 g precision. The size structure (length-frequency distributions, LFDs) indicated that the males with TL 22.0-22.9 cm and females with 29.0-29.9 cm size group were statistically more appeared. The TL and BW varied between 11.5-53.0 cm and 27.6 to 1228.0 g for males, and 18.2-45.0 cm and 57.0 to 728.0 g for females. The length-weight relations (LWRs) were significantly correlated (p < 0.0001), with values of r2 ≥ 0.961. The monthly co-efficient (b) revealed negative allometric growth (< 3.0) of all LWRs for both sexes, excluding males showed isometric growth in December (TL vs. BW). Additionally, length-length relationships (LLRs) indicated notable relation (p < 0.0001), with all r2 ≥ 0.991. The estimated Lm was 27.82 and 23.92 cm for male and female of M. cordyla, separately. The assessed Lopt were 24.87 cm for females and 29.13 cm for males. Accordingly, this research will be a guide to the study of stock assessment, physiology, and biology for M. cordyla in the BoB and the related ecosystems.


Received | April 07, 2022; Accepted | October 18, 2022; Published | December 17, 2022

*Correspondence | Md. Yeamin Hossain, Department of Fisheries, University of Rajshahi, Rajshahi- 6205, Bangladesh; Email: hossainyeamin@gmail.com

Citation | Sarmin, M.S., M.A. Rahman, M.F. Parvin, M.S. Khatun, K.A. Habib, W. Sabbir, J. Ohtomi and M.Y. Hossain. 2022. Temporal variation of biometric indices for Megalaspis cordyla (Linnaeus, 1758) from the bay of Bengal, Bangladesh. Sarhad Journal of Agriculture, 38(5): 300-310.

DOI | https://dx.doi.org/10.17582/journal.sja/2022/38.5.300.310

Keywords | Bay of Bengal (BoB), Growth pattern, Megalaspis cordyla, Population structure, Size at sexual maturity

Copyright: 2022 by the authors. Licensee ResearchersLinks Ltd, England, UK.

This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).



Introduction

Carangid is identified as the main pelagic fisheries resource in the Bay of Bengal. Megalaspis cordyla (Linnaeus, 1758) is a migratory pelagic species, found through inshore and offshore oceanic waters, with depths ranging from around 20 to 100 meters (Al-Sakaff and Esseen, 1999). Torpedo scad forms most of the carangid catches as a dominant species. This species has a good quality of flesh and is marketed in fresh, salted, and dried conditions (FAO, 2009). M. cordyla is abundant in the tropical and subtropical Indian Ocean as well as the west Pacific Ocean (Smith-Vaniz, 1999). This species is found from the South-East African coastline to the Persian Gulf along with the Red Sea (Froese and Pauly, 2021). Trawls, purse seines, and drift gill nets are popular methods of catching this species (Sivakami, 1995). The maximum size was recorded as 80 cm (Smith-Vaniz, 1984) and the body weight was found 4 kg (Bykov, 1983), although it is common at lengths of 45 cm (Bouhlel, 1988).

Length-frequency distributions (LFDs) are an essential biometric criterion for detecting dynamic recruitment, growth, and mortality rates (Neuman and Allen, 2001). Also, LFD is an important indicator of stock status, and spawning period, including the ecology of fish (Ranjan et al., 2005; Khatun et al., 2019). Besides, LFD is useful for the comparison of morphology within species or populations of definite species from varied inhabitants (Hossain et al., 2013). Furthermore, length-weight relationships (LWRs) are crucial for assessing fish well-being and identifying potential discrepancies between various unit stocks (Hossain et al., 2010; Parvin et al., 2021; Sarmin et al., 2021a), while also essential for determining stock status, biomass, and maximum sustainable yield (Anderson and Gutreuter, 1983; Rahman et al., 2020; Sarmin et al., 2021b; Sabbir et al., 2022). Moreover, the length-length relationships (LLRs) are significant as a number of physiological features are related to length (Sabbir et al., 2020). The maturity length (Lm) is the most significant attribute to explain the reproductive biology of fish species that aid in the conservation and sustainable management of fish stock. Fish’s sexual maturity length is used to determine the lowest-permeable size to catch (Parvin et al., 2022) and is crucial in identifying the causes of changes in maturity size (Templeman, 1987). The Lopt aids in the fishing gear selection with appropriate mesh sizes and the restriction of catching fish below this permissible catch size for sustainable management (Mawa et al., 2021).

Some studies with different aspects of M. cordyla have been carried out from worldwide waterbodies but knowledge on size structure, growth pattern, and sexual maturity for this species are very limited in the Bay of Bengal (BoB) from Bangladesh. As a consequence, this study revealed the precise explanation of population size structure, monthly variations of length-weight and length-length relationships, and length of maturity for M. cordyla in the BoB exploited by seine net and drift gillnet units to provide necessary details for proper management of the species.

Materials and Methods

Sampling and data collection

The individuals of M. cordyla (male, 720 and female, 793) were sampled from the Bay of Bengal by commercial fishers with seine nets (mesh size of 1.5 to 3 cm) and gill nets (mesh size of 3 cm) during January to December 2020. The specimens of different size groups were collected randomly. For each sample, body weight (BW) and lengths (total, TL; fork, FL; standard, SL) were recorded with an electronic weighing balance and the standard fish measuring board to 0.01 g accuracy and 0.01 cm, respectively.

Population structure and growth pattern

Population structure through LFDs for M. cordyla was assembled with TL of 1 cm intervals. The growth pattern was obtained by the equation of LWRs: W = a×Lb, where W points to body weight (g) and L denotes lengths (TL, FL, and SL) in cm. Based on natural logarithms, the parameters a and b were obtained through the linear regression analysis: ln (W) = ln (a) + b ln (L). A t-test was done to check how the calculated b values were significantly altered from 3.0 (Sokal and Rohlf, 1987), specifying isometric growth (b = 3.0), and allometric growth (b > 3.0, positive), or (b < 3.0, negative) (Tesch, 1971; Das et al., 2014). The LLRs (TL vs. FL, SL) have also been evaluated with the analysis of linear regression.

Maturity length (Lm)

The Lm for M. cordyla was obtained following log (Lm) = -0.1189 + 0.9157* log (Lmax), where Lmax indicates the maximum length recorded (Binohlan and Froese, 2009). The length of optimum catchable size (Lopt) was calculated by log (Lopt) = 1.053*log (Lm)-0.0565 (Froese and Binohlan, 2000). Besides, the maximum lengths of diverse populations were derived from accessible data to describe the size of sexual maturity as well as optimum catchable size in aquatic bodies all over the world.

Statistical analysis

We used Microsoft® Excel-add-in-DDXL and GraphPad Prism 6.5 software to conduct statistical analyses in all cases with the significance level of 5%. The homogeneity and normality of the data were checked by the Shapiro-Wilk test. The test of Mann-Whitney U was followed to link the mean values of the two sexes. The Spearman rank correlation test has been considered to examine the LWRs and LLRs for male and female.

Results and Discussion

Population structure

The length frequency (LFDs) of M. cordyla revealed that the size range was 11.9-53.9 and 18.9-45.9 cm TL for males and females, respectively. Further, the population showed that 22.0-22.9, 28.0-28.9, 29.0-29.9 cm of TL size groups contain 51, 50, 50 individuals for male indicated dominant group and 29.0-29.9 and 30.0-30.9 cm group with 68 and 61 individuals were precisely dominant for the female population, respectively (Figure 1). Furthermore, Mann-Whitney U-test revealed significant variances between males and females for LFD (U = 219764, p = 0.0001). The TL ranged between 10.5-53.0 cm for males, while 18.2-45.0 cm for females (Figure 2). In this study, also the BW varied from 27.6 to 1228.0 g for the male population and 57.0 to 728.0 g for females (Table 1). Besides, Mann-Whitney U-test indicated that the BW of both sexes was significantly different (Mann-Whitney U = 213311, p = 0.0001).

 

 

 

Growth pattern

The study further stated that the overall, as well as monthly b values for both males and females specified negative allometric growth (b < 3.0) (Figure 3). However, males exhibited isometric growth (b = 3.0) in December. The variances in the “b” value were observed from 2.35 to 3.0 with the correlation coefficient (r2) of 0.927 to 0.987 for all LWRs. The monthly sample size (n), regression parameters with 95 percent confidence limit of the LWRs, and r2 values of M. cordyla were presented in Tables 2, 3, 4. Followed by the Spearman rank correlation test, BW and TL, FL, SL had identical significant relationships. Moreover, ANCOVA revealed statistical differences in LWRs between the male and female populations (p < 0.0001). The LLRs (TL vs. FL, SL) showed prominent relation (p < 0.0001), with r2 ≥ 0.960 (Tables 5, 6 and Figure 4). The LWRs were extremely significant (p < 0.0001), with the values of r2 ≥ 0.961 (Table 7). Also, the Spearman rank correlation test presented substantial relationships among TL and FL, SL (Table 7).

 

Table 1: Descriptive statistics on the length (cm) and weight (g) measurements of male and female Megalaspis cordyla (Linnaeus, 1758) in the Bay of Bengal, Bangladesh during January–December, 2020.

Months

Sex

n

TL (cm)

BW (g)

Min

Max

Mean ± SD

95% CL

Min

Max

Mean ± SD

95% CL

January

M

25

17.0

29.5

22.46±2.97

21.23-23.68

57.21

302.0

133.81±52.07

112.32-155.31

F

40

20.0

29.4

24.16±2.70

23.30-25.03

98.94

293.0

165.24±50.33

149.15-181.34

February

M

52

17.0

33.8

23.93±3.85

22.86-25.00

50.00

353.0

157.23±69.26

137.95-176.51

F

48

20.0

34.0

25.13±3.70

24.06-26.21

92.00

358.0

182.03±70.64

161.52-202.54

March

M

59

17.0

33.0

24.03±3.74

23.06-25.01

77.00

432.0

178.31±73.62

159.12-197.49

F

86

19.0

34.5

24.92±3.73

24.13-25.72

85.00

437.0

192.09±84.92

173.89-210.30

April

M

50

18.0

35.0

24.46±4.60

23.15-25.77

57.00

319.0

139.10±70.92

118.94-159.26

F

56

21.0

35.0

26.79±4.21

25.66-27.91

83.00

360.0

174.84±73.07

155.27-194.41

May

M

57

18.5

36.0

26.89±5.02

25.56-28.22

65.00

351.0

172.53±79.92

151.32-193.73

F

61

18.2

37.0

26.36±5.26

25.01-27.70

57.00

388.0

172.89±94.38

148.71-197.06

June

M

70

20.0

38

28.68±4.00

27.72-29.63

85.00

458.0

210.2±77.12

119.81-228.59

F

81

22.0

38.8

30.76±3.91

29.89-31.62

112.0

470.0

256.40±85.21

237.55-275.24

July

M

73

21.0

42.5

30.89±5.02

29.32-31.66

84.00

546.0

254.74±107.5

229.65-279.83

F

79

23.0

42.0

31.53±4.85

30.44-32.62

96.00

544.0

275.81±113.0

252.50-301.13

August

M

75

19.8

53.0

28.76±6.45

27.28-30.24

73.04

1228

226.22±177.9

185.28-267.17

F

63

22.0

45.0

30.42±5.93

28.93-31.91

98.50

728.0

261.71±145.2

225.15-298.27

September

M

66

11.5

37.4

24.88±6.96

23.17-26.59

27.60

455.0

171.29±109.2

144.44-198.14

F

57

20.2

37.0

28.11±4.31

26.96-29.25

93.00

440.0

217.81±86.56

194.84-240.77

October

M

51

14.0

36.0

22.56±5.52

21.01-24.11

36.08

406.0

122.15±83.87

98.56-145.74

F

60

20.5

37.0

28.53±4.13

27.46-29.59

90.00

445.0

210.07±82.15

188.85-231.30

November

M

81

16.8

37.5

26.02±5.67

24.77-27.28

45.19

504.0

211.21±111.3

186.60-235.82

F

92

20.8

38.9

28.90±4.15

28.04-29.76

120.0

535.0

265.31±95.38

245.56-285.06

December

M

61

16.0

41.0

24.29±7.50

22.37-26.21

38.0

568.0

163.00±148.3

125.02-200.98

F

70

20.0

40.8

30.49±5.56

29.16-31.82

78.35

554.0

276.92±119.3

248.49-305.36

 

n, sample size; M, male; F, female; TL, total length; BW, body weight; Min, minimum; Max, maximum; SD, standard deviation; CL, confidence limit for mean values.

 

 

Maturity length (Lm)

Based on maximum TL, the Lm of M. cordyla was evaluated as 27.82 cm with 95% CL = 18.86-41.05 cm for males and 23.92 cm with 95% CL = 16.35-35.01 cm for females (Figure 5). The calculated Lopt were 24.87 cm for males and 29.13 cm for the female population in the Bay of Bengal. Also, estimated Lm and Lopt from worldwide different populations are shown in Table 8 and Figure 6.

The current research describes the size-frequency distributions and growth pattern of M. cordyla from the Bay of Bengal, Bangladesh with year-round data. A total of 1513 samples of various body sizes were sampled for twelve months. However, smaller than 11.5 cm TL could not be caught, which may be related to inappropriate fishing equipment or a shortage of smaller size of M. cordyla (Hossain et al., 2016, 2021;

 

Table 2: Estimated parameters of the length-weight relationship (BW = a×TLb) of Megalaspis cordyla (Linnaeus, 1758) in the Bay of Bengal, Bangladesh.

Mon-ths

Sex

n

Regression parameters

95% CL of a

95% CL of b

r2

GT

a

b

January

M

25

0.0289

2.70

0.0153-0.0544

2.50-2.90

0.970

A-

F

40

0.0469

2.56

0.0262-0.0837

2.37-2.74

0.955

A-

February

M

52

0.0314

2.66

0.0195-0.0506

2.51-2.82

0.962

A-

F

48

0.0468

2.55

0.0290-0.0758

2.40-2.70

0.962

A-

March

M

59

0.0798

2.41

0.0485-0.1313

2.25-2.57

0.943

A-

F

86

0.0278

2.73

0.0192-0.0403

2.62-2.85

0.964

A-

April

M

50

0.0352

2.57

0.0256-0.0485

2.47-2.67

0.982

A-

F

56

0.0275

2.65

0.0193-0.0391

2.54-2.75

0.978

A-

May

M

57

0.0406

2.52

0.0309-0.0534

2.44-2.60

0.985

A-

F

61

0.0255

2.67

0.0196-0.0333

2.59-2.75

0.987

A-

June

M

70

0.0414

2.53

0.0282-0.0608

2.42-2.65

0.966

A-

F

81

0.0348

2.59

0.0254-0.0477

2.50-2.68

0.975

A-

July

M

73

0.0299

2.63

0.0204-0.0438

2.52-2.74

0.969

A-

F

79

0.0298

2.63

0.0222-0.0399

2.55-2.72

0.980

A-

August

M

75

0.0284

2.64

0.0215-0.0376

2.56-2.72

0.982

A-

F

63

0.0306

2.63

0.0225-0.0416

2.54-2.72

0.982

A-

September

M

66

0.0460

2.51

0.0340-0.0624

2.42-2.61

0.977

A-

F

57

0.0603

2.44

0.0379-0.0961

2.30-2.58

0.957

A-

October

M

51

0.0303

2.62

0.0217-0.0423

2.52-2.73

0.978

A-

F

60

0.0389

2.55

0.0271-0.0560

2.44-2.66

0.974

A-

November

M

81

0.0354

2.64

0.0232-0.0538

2.51-2.77

0.954

A-

F

92

0.0620

2.47

0.0388-0.0991

2.33-2.61

0.932

A-

December

M

61

0.0088

3.00

0.0058-0.0131

2.87-3.13

0.974

I

F

70

0.0665

2.42

0.0493-0.0898

2.33-2.51

0.978

A-

a, intercept; b, slope; r2, coefficient of determination; GT, growth type; A-, negative allometric; I, isometric growth.

 

 

Islam et al., 2021). The maximum TL was found 53.0 cm in males and 45.0 cm in the female population, which is smaller than 80.0 cm reported by Smith-Vaniz (1984) and higher than 43.1 cm from the North-west coast of India (Jaiswar and Acharya, 1991); 40.2 cm from Ratnagiri coast, Maharashtra, India (Jadhav and Mohite, 2013); 40.1 cm from Mumbai coast, India (Saker et al., 2004); 34.4 cm FL from the Java Sea, Indonesia (Oktaviani et al., 2020); and Zafar et al. (2000) found 35.0 cm in the Bay of Bengal, Bangladesh. However, maximum length data is necessary for defining asymptotic length and growth co-efficient of fish to develop appropriate fisheries management policies (Ahmed et al., 2012; Khatun et al., 2019).

 

Table 3: Estimated parameters of the length-weight relationship (BW = a×FLb) of Megalaspis cordyla (Linnaeus, 1758) in the Bay of Bengal, Bangladesh.

Mon-ths

Sex

n

Regression parameters

95% CL of a

95% CL of b

r2

GT

a

b

January

M

25

0.0366

2.71

0.0163-0.0822

2.44-2.98

0.950

A-

F

40

0.0478

2.63

0.0245-0.0933

2.41-2.85

0.941

A-

February

M

52

0.0485

2.62

0.0286-0.0824

2.44-2.79

0.948

A-

F

48

0.0647

2.53

0.0353-0.1186

2.34-2.73

0.937

A-

March

M

59

0.0983

2.42

0.0592-0.1634

2.25-2.58

0.938

A-

F

86

0.0303

2.79

0.0199-0.0462

2.65-2.92

0.952

A-

April

M

50

0.0513

2.52

0.0359-0.0734

2.40-2.63

0.976

A-

F

56

0.0452

2.57

0.0316-0.0647

2.45-2.68

0.975

A-

May

M

57

0.0536

2.51

0.0393-0.0732

2.41-2.60

0.980

A-

F

61

0.0384

2.62

0.0293-0.0503

2.53-2.71

0.985

A-

June

M

70

0.0436

2.59

0.0293-0.0649

2.47-2.71

0.963

A-

F

81

0.0525

2.54

0.0355-0.0778

2.42-2.66

0.959

A-

July

M

73

0.0464

2.57

0.0322-0.0669

2.46-2.68

0.968

A-

F

79

0.0443

2.58

0.0320-0.0612

2.49-2.68

0.974

A-

August

M

75

0.0439

2.59

0.0335-0.0574

2.50-2.67

0.981

A-

F

63

0.0449

2.59

0.0323-0.0626

2.49-2.69

0.978

A-

September

M

66

0.0585

2.51

0.0452-0.0759

2.43-2.60

0.982

A-

F

57

0.0859

2.41

0.0545-0.1354

2.27-2.55

0.955

A-

October

M

51

0.0490

2.55

0.0343-0.0701

2.43-2.67

0.974

A-

F

60

0.0649

2.47

0.0434-0.0971

2.34-2.59

0.965

A-

November

M

81

0.0615

2.55

0.0408-0.0926

2.42-2.68

0.950

A-

F

92

0.0695

2.51

0.0452-0.1068

2.38-2.65

0.941

A-

December

M

61

0.0183

2.87

0.0130-0.0257

2.76-2.98

0.978

A-

F

70

0.1049

2.36

0.0776-0. 141

2.26-2.45

0.975

A-

For abbreviations see Table 2.

 

Table 4: Estimated parameters of the length-weight relationship (BW = a×SLb) of Megalaspis cordyla (Linnaeus, 1758) in the Bay of Bengal, Bangladesh.

Mon-ths

Sex

n

Regression parameters

95% CL of a

95% CL of b

r2

GT

a

b

January

M

25

0.0651

2.59

0.0297-0.1427

2.32-2.86

0.945

A-

F

40

0.0444

2.73

0.0208-0.0946

2.48-2.98

0.927

A-

February

M

52

0.0519

2.68

0.0292-0.0922

2.49-2.88

0.939

A-

F

48

0.0819

2.54

0.0461-0.1455

2.35-2.73

0.940

A-

March

M

59

0.1351

2.38

0.0819-0.2228

2.22-2.55

0.934

A-

F

86

0.0428

2.75

0.0287-0.0639

2.62-2.88

0.953

A-

April

M

50

0.0601

2.55

0.0435-0.0830

2.44-2.66

0.979

A-

F

56

0.0623

2.55

0.0440-0.0882

2.43-2.66

0.974

A-

May

M

57

0.0675

2.51

0.0517-0.0883

2.42-2.59

0.984

A-

F

61

0.0437

2.66

0.0333-0.0575

2.57-2.75

0.984

A-

June

M

70

0.0612

2.56

0.0375-0.0998

2.40-2.71

0.941

A-

F

81

0.0646

2.55

0.0412-0.1013

2.41-2.69

0.944

A-

July

M

73

0.0522

2.60

0.0357-0.0763

2.48-2.72

0.965

A-

F

79

0.0446

2.65

0.0316-0.0630

2.55-2.76

0.970

A-

August

M

75

0.0589

2.57

0.0423-0.0821

2.46-2.68

0.970

A-

F

63

0.0625

2.56

0.0434-0.0900

2.45-2.68

0.971

A-

September

M

66

0.0763

2.51

0.0597-0.0974

2.42-2.59

0.983

A-

F

57

0.1052

2.41

0.0682-0.1623

2.28-2.55

0.957

A-

October

M

51

0.0719

2.51

0.0501-0.1033

2.38-2.63

0.971

A-

F

60

0.0801

2.48

0.0526-0.1221

2.35-2.61

0.960

A-

November

M

81

0.0764

2.55

0.0504-0.1158

2.42-2.69

0.946

A-

F

92

0.0788

2.55

0.0498-0.1246

2.40-2.69

0.931

A-

December

M

61

0.0200

2.92

0.0137-0.0292

2.80-3.05

0.973

A-

F

70

0.1325

2.35

0.0962-0.1826

2.25-2.45

0.970

A-

For abbreviations see Table 2.

 

 

In our analysis, we found that the 22.0-22.9 cm of the TL size group contains the higher number of individuals (51) along with 28.0-28.9 and 29.0-29.9 cm size groups containing 50 individuals for male indicated dominant group. For the female population, the 29.0-29.9 cm group with 68 and 30.0-30.9 cm class with 61 individuals were precisely dominant, and then gradually lowering the number of individuals in the size group which related to the mortality (natural or fishing). Qamar et al. (2016) reported the maximum 91 individuals in the 22.0-25.9 cm length class which is relatively similar to our observation.

 

Table 5: Estimated parameters of total and fork length relationship (TL = a + b × FL) of Megalaspis cordyla (Linnaeus, 1758) in the Bay of Bengal, Bangladesh.

Months

Sex

n

Regression parameters

95% CL of a

95% CL of b

r2

a

b

January

M

25

0.024

1.10

-1.907 to 1.954

1.01 to 1.19

0.962

F

40

-0.517

1.13

-1.779 to 0.746

1.07 to 1.18

0.977

February

M

52

0.657

1.08

-0.165 to 1.480

1.05 to 1.12

0.985

F

48

0.179

1.10

-0.962 to 1.320

1.05 to 1.15

0.977

March

M

59

0.299

1.09

-0.460 to 1.058

1.05 to 1.12

0.986

F

86

-0.231

1.11

-0.946 to 0.483

1.08 to 1.14

0.983

April

M

50

0.661

1.06

-0.006 to 1.328

1.03 to 1.09

0.991

F

56

1.033

1.05

0.241 to 1.825

1.02 to 1.08

0.988

May

M

57

0.228

1.09

-0.482 to 0.938

1.06 to 1.12

0.991

F

61

0.724

1.07

0.078 to 1.370

1.04 to 1.09

0.991

June

M

70

0.009

1.10

-0.932 to 0.950

1.06 to 1.14

0.982

F

81

0.875

1.07

-0.071 to 1.820

1.03 to 1.10

0.981

July

M

73

0.884

1.06

0.155 to 1.612

1.03 to 1.08

0.990

F

79

0.761

1.06

0.107 to 1.415

1.04 to 1.09

0.992

August

M

75

1.423

1.05

0.810 to 2.035

1.03 to 1.07

0.991

F

63

0.585

1.08

-0.086 to 1.255

1.06 to 1.10

0.993

September

M

66

0.239

1.09

-0.128 to 0.606

1.07 to 1.10

0.997

F

57

0.540

1.08

-0.100 to 1.180

1.06 to 1.11

0.993

October

M

51

0.649

1.07

0.158 to 1.139

1.05 to 1.10

0.994

F

60

1.058

1.06

0.258 to 1.858

1.03 to 1.09

0.988

November

M

81

0.827

1.07

0.364 to 1.291

1.05 to 1.09

0.994

F

92

-0.133

1.11

-0.768 to 0.502

1.09 to 1.13

0.989

December

M

61

1.396

1.05

1.001 to 1.792

1.03 to 1.06

0.996

F

70

1.200

1.06

0.412 to 1.990

1.03 to 1.09

0.988

 

According to Carlander (1969), b values may vary from 2.0 to 4.0 for fishes. Instead, Froese (2006) stated that the b values extended from 2.5 to 3.5 of LWRs. We found b values from 2.4 to 3.0 (b = 2.41 to 3.0 for males and b = 2.42 to 2.73 for females), which is similar to the range observed in teleost fishes and that indicated the large specimens’ body form has changed to become more elongated (Froese, 2006; Hossain et al., 2015). Furthermore, b values revealed the growth of negative allometric for both sexes in our research. The b value for combined sex was also negative allometric reported by Jaiswar and Acharya (1991) from the North-west coast of India (b = 2.98); Reuben et al. (1992) from the east, north-west and south-west coast of India (b = 2.94, 2.52, 2.72); Sivakami (1995) from Cochin, India (b = 2.69); Saker et al. (2004) from Mumbai coast, India (b = 2.88); Das et al. (2014) from Tanjung Sepat, Selangor, Malaysia (b = 2.64); Qamar et al. (2016) from Northern Arabian Sea coast of Pakistan ( b = 2.82 for male and 2.45 for female) and Zafar et al. (2000) from Bay of Bengal (b = 2.82) for M. cordyla. But dissimilar results found by Panda et al. (2011) from Mumbai, India (b = 3.02) signified isometric growth and Oktaviani et al. (2020) reported positive allometric growth from the Java Sea, Indonesia (b = 3.15). Though in the same species, b values may differ for various factors such as sex, gonadal development, growth variances in parts of the body, physiology and food accessibility, and preservation techniques (Le Cren, 1951; Tesch, 1968; Hossain et al., 2015), those were not taken into account in our study. Moreover, the LLRs were highly related, but owing to inadequate information on M. cordyla, it was hard to ascertain any comparisons.

 

Table 6: Estimated parameters of total and standard length relationship (TL = a + b × SL) of Megalaspis cordyla (Linnaeus, 1758) in the Bay of Bengal, Bangladesh.

Mon-ths

Sex

n

Regression parameters

95% CL of a

95% CL of b

r2

a

b

January

M

25

0.595

1.17

-1.199 to 2.389

1.07 to 1.26

0.966

F

40

-1.288

1.26

-2.996 to 0.420

1.18 to 1.35

0.960

February

M

52

0.077

1.23

-0.875 to 1.029

1.18 to 1.28

0.981

F

48

0.349

1.21

-0.823 to 1.521

1.15 to 1.27

0.976

March

M

59

0.579

1.17

-0.400 to 1.52

1.13 to 1.22

0.976

F

86

0.098

1.19

-0.653 to 0.849

1.15 to 1.22

0.981

April

M

50

0.340

1.19

-0.440 to 1.121

1.15 to 1.23

0.988

F

56

1.225

1.15

0.371 to 2.079

1.11 to 1.19

0.986

May

M

57

0.416

1.19

-0.422 to 1.255

1.15 to 1.22

0.987

F

61

0.395

1.19

-0.301 to 1.090

1.16 to 1.22

0.990

June

M

70

0.426

1.19

-0.983 to 1.834

1.13 to 1.25

0.960

F

81

1.009

1.17

-0.269 to 2.287

1.12 to 1.22

0.965

July

M

73

0.885

1.15

-0.038 to 1.808

1.12 to 1.19

0.983

F

79

0.132

1.19

-0.846 to 1.11

1.05 to 1.22

0.982

August

M

75

1.629

1.14

0.854 to 2.404

1.11 to 1.18

0.986

F

63

0.857

1.18

0.017 to 1.698

1.14 to 1.21

0.988

September

M

66

0.377

1.19

-0.155 to 0.909

1.17 to 1.22

0.993

F

57

0.673

1.18

-0.275 to 1.620

1.14 to 1.22

0.984

October

M

51

1.181

1.15

0.556 to 1.806

1.12 to 1.19

0.990

F

60

0.953

1.17

-0.032 to 1.937

1.13 to 1.21

0.982

November

M

81

0.700

1.18

0.174 to 1.226

1.16 to 1.21

0.992

F

92

-0.480

1.23

-1.439 to 0.478

1.19 to 1.27

0.977

December

M

61

0.959

1.17

0.460 to 1.459

1.15 to 1.19

0.994

F

70

1.293

1.16

0.434 to 2.153

1.13 to 1.19

0.986

 

Table 7: Spearman rank correlations of body weight with lengths and length with lengths for Megalaspis cordyla (Linnaeus, 1758) in the Bay of Bengal, Bangladesh.

Relationships

Sex

rs values

95% CL of rs

p values

Significance

BW vs. TL

M

0.971

0.967 to 0.975

< 0.0001

***

F

0.966

0.960 to 0.970

< 0.0001

***

BW vs. FL

M

0.970

0.965to 0.974

< 0.0001

***

F

0.961

0.955 to 0.966

< 0.0001

***

BW vs. SL

M

0.968

0.963 to 0.972

< 0.0001

***

F

0.962

0.956 to 0.967

< 0.0001

***

TL vs. FL

M

0.993

0.992 to 0.994

< 0.0001

***

F

0.991

0.990 to 0.993

< 0.0001

***

TL vs. SL

M

0.996

0.995 to 0.996

< 0.0001

***

F

0.995

0.994 to 0.995

< 0.0001

***

rS, Spearman rank correlation values; CL, confidence limit; p, shows the level of significance; ***, highly significance relationship.

 

Additionally, the study provides information on the sexual maturity length of M. cordyla, which could be useful in calculating the mesh size to avoid catching mature smaller individuals and allowing them to spawn. Our estimated maturity size (Lm) of M. cordyla was 27.82 cm in total length for males and 23.92 cm in females. Information on Lm for the fishes in Bangladesh is scarce but Qamar and Panhwar (2018) reported the Lm was 27.0 cm for male and 26.5 cm for female from the Northern Arabian Sea coast, Pakistan, Reuben et al. (1992) found 25.0 cm from the east, north-west and south-west coast of India, and Jadhav and Mohite (2013) observed Lm at 21.0 cm from Ratnagiri coast of Maharashtra, India. Based on the maximum total length we tried to assess Lm from different available worldwide literature. The estimated results are slightly diverse from our study which may be due to the seasonal variation in the water depth that also impacts on nutrient cycling, and energy cycling of aquatic habitat that influences the reproductive ability of fish (Lowerre-Barbieri, 2011; Rahman et al., 2020).

According to our findings, approximately half of the fish spawned when their length was 23.92 cm for females and 27.82 cm for males; fish smaller than those sizes are strictly avoided to catch. The values of Lopt were estimated as 24.87 and 29.13 cm for females and males, respectively, suggesting the size range where optimum yield might be reached; therefore, fish larger than 24.87 cm (TL) are encouraged for exploitation. As a consequence, we aim to protect maximum brood females for their future sustainable yield.

 

Table 8: Estimated length at sexual maturity (Lm) and Lopt of Megalaspis cordyla (Linnaeus, 1758) from different worldwide water bodies.

Authors

Study Area

Sex

TLmax

(cm)

Regression parameter

Lm (cm)

Lopt (cm)

a

b

Jaiswar and Aciiarya, (1991)

North-west coast of India

C

43.1

0.00910

2.98

23.00

23.85

Reuben et al. (1992)

East coast of India

North-west coast of India

South-west coast of India

C

-

-

-

0.000012

0.000127

0.00005

2.94

2.52

2.72

25.00

-

-

26.03

-

-

Sivakami, (1995)

Cochin, India

M

F

C

-

-

-

0.01740

0.00870

0.01340

2.58

2.86

2.69

-

-

-

-

Saker et al. (2004)

Mumbai coast, India

M

F

C

-

-

40.1

0.00007

0.00020

0.00001

2.64

2.46

2.88

-

-

21.50

-

-

22.21

Panda et al. (2011)

Mumbai, India

M

F

C

-

-

36.4

0.01120

0.02100

0.00860

2.92

3.08

3.02

-

-

19.67

-

-

20.22

Jadhav and Mohite (2013)

Ratnagiri coast of Maharashtra, India

C

40.2

-

-

21.00

21.67

Oktaviani et al. (2020)

Java Sea, Indonesia

C

35.4(FL)

0.00700

3.15

19.17

19.68

Das et al. (2014)

Tanjung Sepat, Selangor, Malaysia

M

F

35.5

37.5

0.03400

0.02100

2.65

2.77

19.22

20.21

19.74

20.81

Qamar et al. (2018)

Northern Arabian Sea coast of Pakistan.

M

F

-

-

-

-

-

-

27.00

26.50

28.23

27.86

Zafar et al. (2000)

Bay of Bengal, Bangladesh

C

35.0

0.01790

2.82

18.97

19.47

Present study

Bay of Bengal, Bangladesh

M

F

C

53.0

45.0

53.0

0.03720

0.06000

0.04210

2.58

2.44

2.55

27.82

23.92

27.82

29.13

24.87

29.13

It is our first attempt at this aspect, so evaluation is difficult. But we determined the Lopt for this species following the Lmax values from worldwide literature where we estimated that the smallest Lopt was 19.47 cm for combined sex in the BoB, Bangladesh, and we observed the largest Lopt was 29.13 cm for male from our study.

 

Conclusions and Recommendations

Our research described the population size structure, growth pattern, and maturity of M. cordyla from the BoB, Bangladesh. These findings could be used by fishery biologists to assess the standing stock and biomass of this species in the marine waters of Bangladesh. The optimum catchable-size was strongly recommended to avoid catching fish below that size for conserving the presence of fish from year to year by safeguarding the largest number of brood fish. Moreover, the results will be useful in future research for determining the permitted mesh size of gears, which will aid in the development of justifiable management techniques for M. cordyla in the coastal and marine water.

Acknowledgments

The authors are thankful to the PIU-BARC, NATP-2, PBRG-156 project, and National Science and Technology fellowship (Ministry of Science and Technology, GoB) for their technical and financial support.

Novelty Statement

The present study revealed the optimum catchable size of M. cordyla. The findings would not only serve as a baseline for further studies, especially in the area of coastal and marine water in Bangladesh as well as where outputs are needed, but also would support sustainable management and policy regulations for this species.

Author’s Contribution

Most. Shakila Sarmin: Wrote the manuscript and carried out data analyses.

Md. Ashekur Rahman: Assisted with sampling and data collection.

Most. Farida Parvin: Assisted with data analyses.

Mst. Shefaly Khatun: Helped in laboratory work.

Kazi Ahsan Habib and Wasim Sabbir: Reviewed the manuscript.

Wasim Sabbir: Revised the manuscript.

Md. Yeamin Hossain: Conceptualized this study and developed the method

Conflict of interest

The authors have declared no conflict of interest.

References

Ahmed, Z.F., Hossain, M.Y. and Ohtomi, J., 2012. Modeling the growth of silver hatchet chela, Chela cachius (Cyprinidae) from the Old Brahmaputra River in Bangladesh using multiple functions. Zool. Stud., 51: 336-344.

Al-Sakaff, H. and Esseen, M., 1999. Occurrence and distribution of fish species off Yemen (Gulf of Aden and Arabian Sea). Naga ICLARM Quart., 22(1): 43-47.

Anderson, R. and Gutreuter, S., 1983. Length, weight and associated structural indices. In: Fisheries techniques. Nielsen, L., and Johnson, D., (Eds.). American Fisheries Society, Bethesda, Maryland, USA, pp. 283-300.

Binohlan, C. and Froes, R., 2009. Empirical equations for estimating maximum length from length at first maturity. J. Appl. Ichthyol., 25: 611-613. https://doi.org/10.1111/j.1439-0426.2009.01317.x

Bouhlel, M., 1988. Poissons de Djibouti. Placerville (California, USA): RDA International, Inc, pp. 416.

Bykov, V.P., 1983. Marine Fishes: Chemical composition and processing properties. New Delhi: Amerind Publishing Co. Pvt. Ltd, pp. 322. https://doi.org/10.2306/scienceasia1513-1874.2014.40.317

Carlander, K.D., 1969. Handbook of freshwater fishery biology, Vol. 1. The Iowa State University Press, Ames, IA.

Das, S.K., De, M. and Ghaffar, M.A., 2014. Length-weight relationship and trophic level of hard-tail scad Megalaspis cordyla. Sci. Asia, 40: 317-322.

Fisheries and Agricultural Organisation, 2009. Megalaspis cordyla (Linnaeus, 1758). Species Fact Sheets. FAO. Retrieved 2009-10-21.

Froese, R., 2006. Cube law, condition factor and weight-length relationships: History, meta-analysis and recommendations. J. Appl. Ichthyol., 22: 241-253. https://doi.org/10.1111/j.1439-0426.2006.00805.x

Froese, R. and C. Binohlan. 2000. Empirical relationships to estimate asymptotic length, length at first maturity and length at maximum yield per recruit in fishes, with a simple method to evaluate length frequency data. J. Fish Biol., 56: 758-773.

Froese, R. and Pauly, D., 2021. Fishbase 2021, World Wide Web electronic publication. Available at: http://www.fishbase.org (accessed 27 September 2021).

Hossain, M.Y., 2010. Morphometric relationships of length weight and length length of four Cyprinid small indigenous fish species from the Padma River (NW Bangladesh). Turk. J. Fish. Aquat. Sci., 10: 131-134.

Hossain, M.Y., Paul, A.K., Hossen, M.A., Islam, M.A., Pramanik, M.N.U., Islam, M.A. and Rahman, M.M. 2016. Length-weight relationships of three Gobiidae species from the Rupsha River in southwestern Bangladesh. J. Appl. Ichthyol., 32: 1305-1307. https://doi.org/10.1111/jai.13183

Hossain, M.Y., Rahman, M.A., Rahman, O., Islam, M.A., Rahman, M.A., Hasan, M.R., Mawa, Z., Tanjin, S., Sarmin, M.S., Nima, A., Chowdhury, A.A., Bashar M.A. and Mahmud, Y., 2021. Morphological Characteristics and Length-Weight Relationships of Hilsa shad, Tenualosa ilisha (Hamilton, 1822) in the Ganges River. Acta Zool. Bulg., 74(1): 75-83. http://www.acta-zoologica-bulgarica.eu/2021/002534.

Hossain, M.Y., Rahman, M.M., Abdallah, E.M. and Ohtomi, J., 2013. Biometric relationships of the Pool barb Puntius sophore (Hamilton 1822) (Cyprinidae) from three major Rivers of Bangladesh. Sains Malays., 22: 1571-1580.

Hossain, M.Y., Sayed, S.R.M., Rahman, M.M., Ali, M.M., Hossen, M.A., Elgorban, A.M., Ahmed, Z.F. and Ohtomi, J., 2015. Length-weight relationships of nine fish species from Tetulia River, Southern Bangladesh. J. Appl. Ichthyol., 31: 967-969. https://doi.org/10.1111/jai.12823

Islam, M.A., Hossain, M.Y., Rahman, M.A., Rahman, O., Sarmin, M.S., Khatun, D., Hasan, M.R., Nima, A., Mawa, Z., Rahman, M.A., Tanjin, S. and Parvin, M.F., 2021. Some biological aspects of Asian stinging catfish, Heteropneustes fossilis (Bloch, 1794) (Teleostei: Siluriformes) in a Wetland Ecosystem. Iran. J. Ichthyol., 8 (1): 52-61.

Jaiswar, A.K. and P. Acharya. 1991. Length-weight relationship of Megalaspis cordyla (Linnaeus, 1758) along North west coast of India. J. Indian Fish. Assoc., 21: 45-46.

Jadhav, T.D. and Mohite, S.A. 2013. Reproductive biology of Horse mackerel Megalaspis cordyla (Linnaeus, 1758) along Ratnagiri coast of Maharashtra, India. J. Mar. Biol. Ass. India, 55(2): 35-40. https://doi.org/10.6024/jmbai.2013.55.2.01759-06

Khatun, D., Hossain, M.Y., Rahman, M.A., Islam, M.A., Rahman, O., Sarmin,
M.S., Parvin, M.F., Haque, A.T.U., Mawa, Z. and Hossain, M.A., 2019. Life-history traits of the climbing perch Anabas testeudineus (Bloch, 1792) in a wetland ecosystem. Jordan J. Biol. Sci., 12(2): 175-182.

Le Cren, E.D., 1951. The length-weight relationships and seasonal cycle in gonad weight and condition in the perch (Perca fluviatilis). J. Anim. Ecol., 20 (2): 201-219. https://doi.org/10.2307/1540

Lowerre-Barbieri, S.K., Ganias, K., Saborido-Rey, F., Murua, H. and Hunter, J.R., 2011. Reproductive timing in marine fishes: Variability, temporal scales, and methods. Mar. Coast. Fish., 3(1): 71-91. https://doi.org/10.1080/19425120.2011.556932

Mawa, Z., Hossain, M.Y., Hasan, M.R., Tanjin, S., Rahman, M.A., Sarmin, M.S. and Habib, K.A., 2021. First record on size at sexual maturity and optimum catchable length of 10 marine fishes from the Bay of Bengal (Bangladesh) through multi-models approach: A key for sound fisheries management. Environ. Sci. Pollut. Res., 28: 38117-38127. https://doi.org/10.1007/s11356-021-13491-8

Neuman, R.M. and Allen, M.S., 2001. Analysis and interpretation of freshwater fisheries data. Store, USA: Department of Natural Resources Management and Engineering, University of Connecticut.

Oktaviani, D., Prianto, E.B. and Nugroho, D., 2020. Length-weight, maturity, and condition factor of torpedo scads (Megalaspis cordyla Linnaeus, 1758) in the Java Sea, Indonesia. Biodiversitas, 21(4): 1527-1534. https://doi.org/10.13057/biodiv/d210433

Panda, D, Chakraborty, S.K., Jaiswar, A.K., Sharma, A.P., Jha, B.C., Sawant, B.T., Bhagabati, S.K. and Kumar, T., 2012. Fishery and population dynamics of two species of carangids, Decapterus russelli (Ruppell, 1830) and Megalaspis cordyla (Linnaeus, 1758) from Mumbai waters. Indian J. Fish., 59: 53-60.

Parvin, M.F., Hossain, M.Y., Rahman, M.A., Khatun, D., Sarmin, M.S., Rahman, O., Islam, M.A., Azad, M.A.K., Samad, M.A., Sabbir, W., Kamruzzanan, Sk., Hosneara, U. and Hassan, H.U., 2021. Growth, maturity, condition, size at sexual maturity and mortality of the Banded gourami Trichogaster fasciata from the Ganges River, Northwestern Bangladesh. Egypt. J. Aquat. Biol. Fish., 25(4): 285-299. https://doi.org/10.21608/ejabf.2021.189004

Parvin, M.F., Hossain, M.Y., Sarmin, M.S., Rahman, O., Tanjin, S., Samad, M.A. and Rahman, M.A., 2022. Reproductive performance of Asian stinging catfish Heteropneustes fossilis (Bloch 1794) in the Ganges River (NW Bangladesh) in relation to environmental factors. Environ. Sci. Pollut. Res., 29: 42822–42836). https://doi.org/10.1007/s11356-022-18816-9

Qamar, N. and Panhwar, S.K., 2018. Assessment of maturity, reproduction and reproductive potentials of Torpedo scad, Megalaspis cordyla (Linnaeus, 1758) from Northern Arabian Sea coast of Pakistan. Russ. J. Mar. Biol., 44: 42-50. https://doi.org/10.1134/S1063074018010078

Qamar, N., Panhwar, S.K. and Brouwer, S., 2016. Population characteristics and biological reference point estimates for two Carangid fishes, Megalaspis cordyla and Scomberoides tol, in the Northern Arabian Sea coast of Pakistan. Pak. J. Zool., 48(3): 869-874.

Rahman, M.A., Bashar, M.A., Mawa, Z., Rahman, O., Samad, M.A., E-Mahfuj, M.S., Islam, M.A., Sarmin, M.S., Islam, M.R., and Hossain, M.Y., 2020. Life history traits of the Barred spiny eel Macrognathus pancalus (Hamilton, 1822) in a wetland ecosystem. Egypt. J. Aquat. Biol. Fish., 24(6): 425-438. https://doi.org/10.21608/ejabf.2020.121162

Ranjan, J.B., Herwig, W., Subodh, S. and Michael, S., 2005. Study of the length frequency distribution of Sucker head, Garra Gotyla Gotyla (Gray, 1830) in different rivers and seasons in Nepal and its application. Kathm. Univ. J. Sci. Eng. Tech., 1: 1-14.

Reuben, S., Kasim, H.M., Sivakami, S., Nair, R.P.N., Kurup, K.N., Sivadas, M., Noble, A., Nair, S.K.V. and Raje, S.G. 1992. Fishery, biology, and stock assessment of carangid resources from the Indian seas. Indian J. Fish., 39: 195-234.

Sabbir, W., Hossain, M.Y., Khan, M.N., Rima, F.A., Sarmin, M.S. and Rahman, M.A., 2022. Biometric Indices of Flathead Sillago, Sillaginopsis panijus (Hamilton, 1822) from the Bay of Bengal (Southern Bangladesh). Thalassas: Int. J. Mar. Sci., 2022. https://doi.org/10.1007/s41208-022-00421-9

Sabbir, W., Hossain, M.Y., Rahman, M.A., Hasan, M.R., Khan, M.N., Mawa, Z., Tanjin, S., Sarmin, M.S., Rahman, O., Nima, A. and Habib, K.A., 2020. Growth pattern of the Hooghly Croaker Panna heterolepis Trewavas, 1977 in the Bay of Bengal (Bangladesh) in relation to eco-climatic factors. Egypt. J. Aquat. Biol. Fish., 24(7): 84-862. https://doi.org/10.21608/ejabf.2020.132074

Saker, Y., Jaiswar, A.K., Chakraborty, S.K. and Swamy, R.P., 2004. Morphometry and length-weight relationship of Megalaspis cordyla (Linnaeus, 1758) from Mumbai coast. Indian J. Fish., 51: 481-486. https://doi.org/10.56042/ijms.v50i05.66244

Sarmin, M.S., Hossain, M.Y., Islam, M.A., Rahman, M.A., Khatun, D., Mawa, Z., Chowdhury, A.A. and Ohtomi, J., 2021a. Estimation of population parameters for a data deficient Salmostoma bacaila (Hamilton 1822) stock from the Mahananda river (tributary of the Ganges) in NW Bangladesh. Indian J. Geo-Mar. Sci., 50(5): 403-409.

Sarmin, M.S., Tanjin, S., Rahman, M.A., Hasan, M.R., Sabbir, W., Asadujjaman, M., Mondol, M.R.K., Habib, K.A. and Hossain, M.Y., 2021b. Estimation of growth pattern and form factor of Torpedo scad Megalaspis cordyla (Linnaeus, 1758) in the Bay of Bengal, Bangladesh. Pak. J. Mar. Sci., 30 (2): 109-117. https://www.pakjmsuok.com/index.php/pjms/article/view/103

Sivakami, S. 1995. Fishery and biology of the carangid fish Megalaspis cordyla (Linnaeus) off Cochin. J. Mar. Biol. Ass. India, 37: 237-248.

Smith-Vaniz, W. 1999. Carangidae (PDF). In Carpenter, K.E.; Niem, V.H. (eds.). The living marine resources of the Western Central Pacific Vol 4. Bony fishes part 2 (Mugilidae to Carangidae). FAO species identification guide for fishery purposes. Rome: FAO, pp. 2659-2757.

Smith-Vaniz, W.F., 1984. Carangidae. In Fischer, W., and Bianchi, G., (eds.) FAO species identification sheets for fishery purposes. Western Indian Ocean fishing area 51. Vol. 1. [pag. var.]. FAO, Rome.

Sokal, R.R. and Rohlf, F.J., 1987. Introduction to Biostatistics. 2nd edn. New York: Freeman Publication.

Templeman, W., 1987. Differences in sexual maturity and related characteristics between populations of thorny skate (Raja radiate) from the northwest Atlantic. J. Northwest Atl. Fish. Sci., 7: 155-167. https://doi.org/10.2960/J.v7.a18

Tesch, F.W., 1968. Age and growth. In: Methods for assessment of fish production in freshwaters. Edited by Ricker WE Oxford: Blackwell Scientific Publications.

Tesch, F.W., 1971. Age and growth. In Methods for Assessment of Fish Production in Fresh Waters, edited by Rcker, W.E. Oxford: Balckwell Scientific Publications, pp. 99-130.

Zafar, M., Mustafa, M.G. and Haque, M.A., 2000. Population dynamics of Megalaspis Cordyla (Linnaeus 1758) from Northeastern part of the Bay of Bengal, Bangladesh. Indian J. Fish., 47(3): 163-168. https://doi.org/10.33997/j.afs.2000.13.3.006

To share on other social networks, click on any share button. What are these?

Sarhad Journal of Agriculture

September

Vol.40, Iss. 3, Pages 680-1101

Featuring

Click here for more

Subscribe Today

Receive free updates on new articles, opportunities and benefits


Subscribe Unsubscribe