(Bloch) from Tuticorin waters of Southeast coast

Available online at http://www.urpjournals.com

International Journal of Research in Fisheries and Aquaculture

Universal Research Publications. All rights reserved

ISSN 2277-7729

Original Article

A study of age and growth of Secutor insidiator (Bloch) from Tuticorin waters of

Southeast coast of India.

D.NAGARAJAN

Associate Professor, Dept. of zoology, Kamaraj College, Tuticorin – 628003, Tamil Nadu

Received 29 August 2013; accepted 30 September 2013

Abstract

Age and growth of Ponyfish Secutor insidiator (Bloch) was estimated from the length frequency data. The growth parameters „L ‟, „K‟ and „t

0

‟ were calculated as per Von Bertlanffy, Bagenal, Gulland & Holt, Ford-Walford, Powel and

Wetheral methods and also through FISAT software. Von Bertalanffy growth equation fitted for the length at age data is lt

= 123.8(1-exp-3.1613 (t+0.0007)). S.insidiator

attains a length of 69, 98 and 112 mm in 0.25, 0.5 and 0.75 years. The life span (T max) is estimated to be 0.95 years.

© 2013 Universal Research Publications. All rights reserved

Keywords : Secutor insidiator , Model progressive analysis, Growth parameters, T max

1.

INTRODUCTION

Information on the growth of a fish is an important prerequisite in understanding the dynamics of its populations.

In fishery yield studies, the growth is a basic variable determining the exploitable stock and yield from the fishery. Age and growth studies in fishes help to know the age and class structure of the stock and fluctuations in the fishery caused by the presence or absence of various year classes. In the present study the age length key are derived from the length frequency analysis. Determination of growth parameters of fish requires a reliable age-length key.

The important growth parameters are „L ‟, „K‟ and „t

0

‟.

L is interpreted as “the mean length of very old (strictly: infinitely old) fish” and K is a “curvature parameter” which determines how fast the fish approaches L . The short lived fishes almost reach L in a year or two and have a high value of K. Other species have a flat growth curve with a low K value and need many years to reach L . The third parameter, t

0

also called “the initial condition parameter” determines the point in time when the fish has zero length. Biologically, this has no meaning, because the growth begins at hatching. Owing to the paucity of information on the age and growth of Secutor insidiator for

Gulf of Mannar, the present study was undertaken to estimate the age and growth of this species.

2.

MATERIALS AND METHOD

2.1.

Treatment of the data

The data were collected once in a weak by random sampling method from minimum of 10 trawlers from the

122 commercial fish landings by trawls at Tuticorin fishing harbour along with catch and effort and species composition. Total length of 2741 specimens of

S.insidiator

was measured. The weight of the fish landed was recorded by eye estimation since the fish were auctioned in lots in the auction hall. The length frequency data were grouped into 5 mm class intervals and each length group were raised for the sampling day‟s catch and subsequently for the month‟s catch by respective raising factors as per the method of Sekharan (1962).

2.2.

Model progression analysis (scatter diagram technique)

The integrated method i.e., the simultaneous application of

Peterson‟s method and the Modal progression analysis was used (Pauly, 1980) to identify the various broods in a year and their growth in subsequent period. The length frequency data during 1993-„95 for S.insidiator

are given in

Table 1 and 1a. The modes recognized in the length frequency data for various months are represented in the form of scatter diagram and the progression of mode was traced freehand through time. This line was extrapolated with reference to the inter-modal slope so as to intersect the time axis in order to trace the time of brood origin. This trend line leading from the time axis to the highest modal value in the series was the first guideline for tracing the growth history of the still older broods. When many similar trend lines were fitted, each are acted as guideline for tracing the growth history of the much older broods and also to correct, if necessary already fitted lines for the younger broods. The progression of modes through successive month along a series of trend lines, representing growth of various broods, is given in figure 1. The modes

International Journal of Research in Fisheries and Aquaculture 2013; 3(4): 122-129

thus traced were tabulated chronologically (George and

Banerji, 1968) and the average sizes were calculated as shown in Table 2. The average sizes were plotted on an arithmetic graph against the age in months and a free hand curve was fitted through the plots and this may be considered as an empirical growth curve of the species as shown in figure 2. A fresh set of lengths attained by these species from the first month of its age onwards have been obtained from these empirical growth curves which enables to obtain the missing data at lower and higher size ranges.

These data were used for further analysis to obtain the growth parameters `L ‟, `K‟ and `t

0

‟ as per von Bertlanffy

(1934), Bagenal (1955), Gulland and Holt (1959), Ford-

Walford (1946) and Powel and Wetheral (1987) methods.

Estimates of L , and K were obtained by using FISAT software (Gayanilo et al. 1995) also.

2.3.

The von Bertalanffy growth equation

The mathematical model derived by von Bertalanffy (1938) was used to calculate the length of fishes at any given time.

This equation is based on the concept that the growth is the result of anabolism and catabolism. The mathematical model expresses the length „L‟ as a function of the age of fish,„t‟: lt = L (1-e

-k (t-to)

) --------------------------------------- 1

Where L = asymptotic length, lt = Length at age t, exp = natural logarithm, K = co-efficient katabolism, t = age of fish and t

0

= age at 0 length.

2.4.

Begenal method

Begenal (1955) described the method of fitting von

Bertalanffy‟s equation for estimating the parameters L , K and t

0

. For this purpose von Bertalanffy‟s growth equation was rewritten as lt+1= L (1-e

-K

)+e

-K

lt -------------------------------- 2

This equation gives linear relationship between the lengths

123 at time „t‟ and at time „t+1‟

Where a = L (1-e l t+1

=a+b l

-K

) and b = e t

-k

Applying standard methods of regression analysis the „a‟ and „b‟ for the values of l t

and l t+1

were obtained. For this purpose the equation l t+1

=a+b l t may be written in the general form.

Y = a+bx --------------------------------------------------- 3

N XY - X. Y b =

N X

2

- ( X)

2 a = Y - b x and l t

= X and l t+1

= Y

The value of „K‟ is derived from that of „b‟ using the expression

K = - log e b ------------------------------------------------4 t

0

was estimated by rewriting the von Bertalanffy‟s Growth

International Journal of Research in Fisheries and Aquaculture 2013; 3(4): 122-129

equation as

- k t + k t l t = L - L e

- k t + k t

L e 0 = L - l t

0

L - l t e

- k t + k t

0

=

L

L - l t

- k t + k t o

= log e

L

L - l t k t o

= log e

L

+ k t

L - l t t o

= 1/k { (log e

) + k t } -----------------5

L

2.5.

The Gulland and Holt plot

Growth parameters can be derived from age/length data by graphical methods for plots, which are always based on a conversion to a linear equation. These plots are named after the authors ie.,e Chapman (1961), Ford-Walford

(1946) and von Bertalanffy (1934). The Gulland and Holt

(1959) plot is obtained from the equation

L/ t = K L - K L (t) ----------------------------------6

The length „l(t)‟ represents the length range from l(t) at an age t to l(t+ t) at age t+ t. Thus, the natural quantity to enter into Eq.(6.6) is the mean length Using l(t) as the independent variable and L/ t as the dependent variable

Eq.(6.6) becomes a linear regression:

L/ t = a+b * L (t) l(t+ t) +l(t)

L =

2

The parameters K and L are obtained from K = - b and

L = - a/b

2.6.

The Ford – Walford plot and Chapman‟s method

This method introduced by Ford (1933) and Walford

(1946) was derived from the original growth equation

(Eq.6.1) by a series of algebraic manipulations such as: l(t+ t) = a + b l(t) ---------------------------------------------7

Where a = L (1 – b) and b = exp. (- K t )

Since K and L are constants „a „and also „b‟ become constants if t is a constant. Using l(t) and l(t+ t) as (x,y)

Eq. 6.7 can be used for linear regression. The growth parameters „K‟ and „L ‟ are derived from

K= -(1/ t)

L

*

Lnb and L = a / (1 – b) can be estimated graphically from the intersection point of the regression line and the line l(t) = l(t+ t) (the 45 degree line) because for very old fish, which have stopped growing we have L = l(t) = l(t+ t).

Also the methods described by Chapman (1961) and later by Gulland (1969) are based on a constant time interval„ t‟, that is to say that the method is applicable if we have pairs of observations.

(t, L(t) ), (t+ t, L(t + t)), (t+2 , L(t+2 t)),etc.

It can be shown that the von Bertalanffy growth equation implies that:

L(t+ t) - L(t) = c

*

L - c *L(t) ----------------------------- 8

124

Where c = 1 – exp ( - K

*

t )

Thus, since K and L are constants, and if t remains constant, „C‟ will remain constant and consequently Eq.

(6.8) becomes a linear regression

Y = a + b x where

Y = L(t+ t) - L(t) , a =c

*

L , b = - c and x = L(t)

The growth parameters are derived from

K = - (1/ t)

*

Ln (1 + b) and L = - a/b or a/c

2.7.

Powell – Wetherall method

Powell makes use of variance in length of fish caught from

L

‟ onwards and he proposes the following equation to get L

and Z / K.

L – L‟ = a+b * L‟ where,

L = -a/b and Z /= - (1+b)/b

Thus, plotting L against L‟ gives a linear regression from which a and b can be estimated and hence L and Z / K.

2.8. The von Bertalanffy plot

This method can be used to estimate K and to from age/length data, while it requires an estimate of L as input. The growth equation (6.1) can be rewritten

-Ln (1 - L(t)/L ) = - K

* t

0

+ K

*

t ----------------------------9

With the age, t, as the independent variable (x) and the lefthand side as the dependent variable (y) the equation defines a linear regression, where K represents the slope and -K

*

t

0 the intercept.

K = b and t

0

= - a/b

The growth parameters are also estimated from the length frequency data by using FISAT software. The growth parameters W , K and t

0 in weight of these species is estimated from the corresponding weight obtained for the size at an interval of one month year as per their respective length-weight relationship by the method of Bagenal

(1955).

3.

RESULT

From the length frequency data (Table 1 & 1a) progression of modes can be traced for the period ranging from 2 to 5 months (Fig. 1). A mode at 62.5mm in July 1993 can be traced to 92.5mm in October 1993, and two modes at

67.5mm in January 1994 and July 1994 can be traced to

97.5mm in September 1994 and October 1994 respectively, showing an average growth 10mm per month. Further one mode at 97.5mm in October 1994 can be traced to

102.5mm in November 1994 and two modes at 102.5mm in

December 1994 and August 1994 can be traced to

107.5mm in January 1995 and September 1994 respectively, showing a monthly growth of 5 mm. Monthly growth of 10 mm between 62.5 mm to 97.5 mm in, and 5 mm between 97.5 to 107.5 mm were observed. Hence, the smallest modal length at 62.5 mm (from which growth could be traced) can be reasonably taken as three months old with an average monthly growth of 21mm. The progression of model lengths in successive months during

1993-1995 is given in the Table 2. As per the empirical growth curve (Figure 2) S.insidiator

attains 69, 99 and

112mm in 0.25, 0.5 and 0.75 years with a monthly growth rate of 23.6, 9.3 and 4.3mm respectively.

International Journal of Research in Fisheries and Aquaculture 2013; 3(4): 122-129

Fig. 1. Tracing the progression of modes by scatter diagram of modal length-month for Secutor insidiator for Tuticorin during 1993 - 1995

Table 1.

Estimated numbers for S.insidiator

during 1993 - 1994

Mid length

(mm)

Mar

„93

Apr

„93

May „93 Jun „93 Jul „93 Aug „93

Sep

„93

Oct

„93

Nov „93

Dec

„93

Jan „94

62.50

67.50

72.50

77.50

82.50

87.50

92.50

97.50

102.50

107.50

112.50

117.50

TOTAL

Feb

„94

TOTAL

0

689

0

2066

0

0

0

0

3443 0

24169 47235

34563 55187

10082 50587

3568

689

8531

0

0

0

0

0

0

704737

2401015

1722504

3334643 10660740 2184398

2316876 6179886 6861284

3691666

959854

585774

176875

0

0

0

0

2413639

5397251

4082182

1206252

1261357

0

0

0

134806

134806

1351

279669

5085953

4374594

459287

236935

1351

0

0

0

0

0

166044

1323895

710801

0

0

0

0

0

0

34678

46275

0

92904

87293

0

87293

0

7689

17145

5611

0

0

0

0

122025

667391

2047838 213181 187258 750731

1730977 165813 129272 563869

0

0

30212

48556

33142

14798

15414

23736

2200343 210870 57986 1390289 18959

3382887 256390 15378 1617517 25435

75837

4161

3546

0

6415

14967

10691

2138

4276

2138

7773

29980

29153

15217

4009

738

53709

89515

89515

53709

0

0

318046

1080563

4949353

7559428

35806 16526789

17903 17506880

17903 16853674

0 11928956

0

0

5622515

3023808

783127

6349

79269 161540 15893944 31201307 19754434 11562785 927207 687829 5111822 293796 127495 358060 86159488

Table 1a: Estimated numbers for S.insidiator

during 1994 - 1995

Mid length

(mm)

Mar

„94

Apr

„94

May „94 Jun „94 Jul „94 Aug „94 Sep „94

92.5

97.5

102.5

107.5

112.5

117.5

TOTAL

62.5

67.5

72.5

77.5

82.5

87.5

Oct „94

Nov

„94

Dec

„94

Jan „95 Feb „95 TOTAL

4925 0 0

0

4925

0

0

0

0

0

201389

0

0

0

6478170

4925 201389 6588223

0

56493

112985

225970

112985

508433

10300 0 0

10300

31906

41199

54518

0

0

437825

1167535

0

0

0

0

183147 3940429 913735

0

0

0

0

0

700628

0

0

0

0

0

14764

0

0

0

0

2197

0

0

0

0

0

0

0

0

0

0

0

0

0

15225

66793

149816

704994

8016794

13055673

4925 172619 5772824 1016866 490660 1897244 456868 350314 7382 6592 0 1092481 11268775

9849

0

4925

0

0

14385

28770

0

0

0

517753

110053

0

165080

110053

1129851 352975

451940

112985

56493

0

105011

31906

10300

0

473150

1233541

181267

181267

0

1142169

328406

1970433

328406

328406

875785

175157

1050942

175157

175157

18456

29529 327793 127571 819361

3691

0

0

93232 382713 819361

188835

30345

7185

255142

0

0

273120

0

0

5829679

3737132

4073246

947048

620801

34474 618552 19742156 3785001 1322222 9512258 5468423 3503140 73822 656179 765426 3004323 48485976

International Journal of Research in Fisheries and Aquaculture 2013; 3(4): 122-129 125

Table 2: Progression of model length (mm) in successive months for S.insidiator during 1993-1995

Curve No. Origin

4

5

6

7

1

2

3

8

9

10

11

Mean Length (mm)

March

July

March

April

1

32

33

31

32

32

2

54

55

53

54

54

3

70

70

71

71

70

89

70

73

4

82

82

84

83

82

82

81

82

82

A g e I n M o n t h s

5 6

92

92

92

93

93

92

91

90

91

92

92

101

99

99

101

99

99

98

98

98

98

98

99

7

105

105

106

104

104

104

103

104

104

8

116

111

108

108

108

110

9

113

113

Table 3: Estimated values of t

0

and calculated values of length and weight of S.insidiator by Bagenal‟s method.

Age

(month)

Lt

Total

Length mm (x)

Lt + 1

(Y) t

0

Calculated

Length

(mm)

Empirical

Weight (g)

Cube root of wt(x)

Cube root of wt+1

(y) t

0

Calculated weight

(g)

1

2

3

4

5

6

7

8

32

54

69

82

92

99

104

109

113

54

69

82

92

99

104

109

-0.01127

-0.01461

-0.00782

-0.01015

-0.01332

-0.00864

0.00346

29

51

68

81

91

98

104

113 -0.00528 109

Mean t

112

0

= -0.0085/Month; -0.0007/yr a (intercept) = 28.68 b (slope) = 0.7684

L∞ a/1-b = 123.8 mm K (annual) = 3.1613

95% confidence limits for a: (26.4870, 30.8738)

95% confidence limits for b: (0.7423, 0.7945)

126

0.371

2.087

4.689

8.293

12.128

15.452

18.183

21.234

23.918

0.718

1.278

1.674

2.024

2.298

2.491

2.63

1.278

1.674

2.024

2.298

2.491

2.63

2.769

-0.0022

-0.0046

0.0016

-0.0018

-0.0061

-0.0018

0.0106

0.3

2.0

4.8

8.2

11.9

15.4

18.6

2.769 2.881 0.0042 21.4

2.881

Mean t

0

= -0.00001/Month; -0.0000008/yr

23.7 a (intercept) = 0.7019 b (slope) = 0.7826 w∞ 1/3 = 3.2290 woo = 33.67 K (annual) = 2.9414

95% confidence limits for a: (0.6450, 0.7588)

95% confidence limits for b: (0.7555, 0.8097)

International Journal of Research in Fisheries and Aquaculture 2013; 3(4): 122-129

Table 4: Estimation of growth parameters (L∞, K and t

0

) for S.insidiator during 1993 – 1995 as per Von Bertalanffy,

Ford-Walford, Chapman and Gulland and Holt methods.

Methods Von Bertalanffy Ford-walford Chapman Gulland and Holt t" months

L(t) mm

(x)

L(t+Dt) +L(t)/2

(x)

- Ln (1 - L(t)/L¥)

(y)

L(t +Dt)

(y)

L(t+Dt) - L(t)

(y) dL(t)/dt

(y)

5

6

7

8

9

1

2

3

4

32

54

69

82

92

99

104

109

113

43

61.5

75.5

87

95.5

101.5

106.5

111

0.2991

0.573

0.815

1.0858

1.3592

1.6078

1.833

2.124

2.4391

54

69

82

92

99

104

109

113

22

15

13

10

7

5

5

4

22

15

13

10

7

5

5

4

Von Bertalanfy Ford-Walford Chapman Gulland and Holt a (intercept) = 0.0342 b (Slope) =0. 26285 a (intercept) = 28.6804 b (Slope) = 0.7684 a (intercept) =28.6804 b (Slope) = -.0.2316 a (intercept) = 32.3959 b (Slope) = -0.2614

K (annual) b* 12 = 3.1548 t

0

(annual)

(-a/b)/12 = -0.0108

K (annual)

(-Lnb/dt)* 12 = 3.1613

L∞ a/(1-b)/ = 123.8 mm

K (annual)

Ln(1+b)* 12 = 3.1613

L∞

-a/b = 123.8 mm

K (annual)

-b* 12 = 3.1368

L∞

-a/b = 123.9 mm

Table5.

Estimation of asymptotic length (L∞) for S.insidiator during 1993-1995 as per Powell Wetherall (1987).

L‟= L

1

-L

(X)

2

C(L

1

,L

2

)

(% catch

(L

1

+L

2

)/2

∑ C(L‟,∞)

(% Cumulated)

((L

1

+L

2

)/2)*C

∑(( L

1

+L

2

L‟

)/2)*C L L - L‟

60-65

65-70

70-75

75-80

80-85

85-90*

90-95*

95-100*

100-105*

105-110*

110-115

115-120

0.2475

0.8521

3.7871

6.1379

18.2283

22.6985

20.8863

13.1891

6.9513

5.2709

1.285

0.4658

62.5

67.5

72.5

77.5

82.5

87.5

92.5

97.5

102.5

107.5

112.5

117.5

99.9998

99.7523

98.9002

95.1131

88.9752

70.7469

48.0484

27.1621

13.973

7.0217

1.7508

0.4658

15.46875

57.51675

274.5648

475.6873

1503.835

1986.119

1931.983

1285.937

712.5083

566.6218

144.5625

54.7315

9009.535

8994.066

8936.55

8661.985

8186.298

6682.463

4696.344

2764.361

1478.424

765.9158

199.294

54.7315

90.096

90.164

90.359

91.070

92.007

94.456

97.742

101.773

105.806

109.079

113.831

117.5.1 a (intercept) = 30.8822 sa = 1.6538 95% confidence limits for a = (25.623, 1414) b (slope) = -0.2538 sa

2

=2.7352 95% confidence limits for b = (-0.309, -0.1986)

L∞ = -a/b = 121.7 mm sb = 0.01736 * used in the analysis (n=5)

Z/K = -(1=b)/b = 2.9401 sb

2

= 0.0003

30.096

25.164

20.359

16.07

12.007

9.456

7.742

6.773

5.806

4.079

3.831

2.501

The L , K and t0 obtained by the various methods and their respective Table and Figure numbers are given below:

L

(mm)

123.8

-

123.9

123.8

123.8

121.7

122.0

K

(year)

3.1613

3.1548

3.1368

3.1613

3.1613

-

2.5000 to

(year)

-0.0007

-0.0108

-

-

-

-

-

Method

Bagenal

Von Bertalanffy

Gulland and Holt

Ford-walford

Chapman

Powell wetherall

Bhattacharya-FISAT year

1955

1934

1959

1946

1961

1987

1967

Table

No.

3

4

4

4

4

5

-

Figure

No.

2

3

4

5

6

7

8

124.0 3.0000 - ELEFAN I - FISAT

According to the von Bertalanffy growth equation lt = 123.8(1-exp

-3.1613 (t+0.0007)

)

1995 - 9

S.insidiator

is estimated to grow 68, 98 and 112 mm in 0.25, 0.50, and 0.75 years. The life span (T max) of this species is estimated to be 0.95 years as per the equation: T max = 3/K.

127 International Journal of Research in Fisheries and Aquaculture 2013; 3(4): 122-129

The growth parameters W , K and t

0

of S.insidiator

were given below:

Year Gram

0.25 4.8

Growth parameters

W (g)

K (year)

S.insidiator

33.7

2.9414

0.50

0.75

1.00

W

15.4

23.7

28.6

33.7 t

0

(year) -0.0000008

The growth in weight may be described by the following von-Bertalanffy (1938) growth equations. wt = 33.7(1-exp

-2.9414 (t+0.0000008)

) 3

As per the above equations the weight (in gram) attained at an interval of 0.25 year is given below.

Obtaining a reliable estimates of growth parameters for tropical species is hampered very much due to interference of various factors such as short life span, seasonal variations in growth within a year etc,.

Generally in nature the oldest fish in the stock grows to reach about 95% of its asymptotic length (Beverton, 1963).

Assuming the maximum size encountered in the fishery ie.,

117mm for S.insidiator

and 166 to be 95 % of the L of these then the L works out theoretically to 123 mm.

Present estimates obtained through various methods vary from 122 to 124 mm for and all these estimates are much closed to the theoretical estimates obtained for all the four species as shown above.

The estimates of growth parameters obtained in the present study and earlier work in S.insidiator

in Indian waters are given in the form of a Table here for comparison.

Growth parameters

Locality Author Year

L (mm) K (annual) t

0

(annual)

Tuticorin Present 122-124 2.5 to 3.1613 -0.0108to -0.0007

Kakinada

Portonovo

Kerala coast

Murty

Jayabalan

Abraham

1990

1991

2011

123

120

130

1.2

_

0.80

-0.01

_

-0.001

Murty (1990) has reported the growth parameters for

S.insidiator

from Kakinada to be L = 123mm, K = 1.2 per year and t

0

= -0.01 year which indicate that the L is very close and the K is lower than the present estimates obtained for the same species. Further, as seen from the K of all these species reported by other workers it appears that all these species are exhibiting much slower growth than the four species presently studied.

The short lived species has small L and a high K value and long lived species have a higher L with a low K value

(Pauly, 1985). Present study shows that S.insidiator

is having small L and higher K values indicating that these species are short lived like the Indian mackerel Rastrelliger kanagurta (Yohannan, 1982; George and Banerji, 1968), oil sardine Sardinella longiceps (Banerji, 1973); and barracuda Sphyraena obtusata (Kasim and

Balasubramanian, 1990). The long lived species like seerfish Scomberomorus commerson (Devaraj, 1982) and

Rhizoprionodon acutus (Kasim, 1991) and perch Lethrinus nebulosus (Kasim et al, 1989) have higher L and small K.

Larger perlagic fishes such as the king seer Scomberomorus commerson is reported to attain 500 to 600 mm in 6 months and about 800 mm in 1 year by Dadley et al., (1992) based on the daily growth ring. Faster growth among the tropical species is not uncommon in view of the prevalent high temperature which profoundly influences the growth of the poikilotherms. The same is true for long lived tropical species also as reported by Kasim (1991) in the case of sharks. Naturally it is true from the present study and earlier reports that the silverbellies are small to medium

128 sized fishes with short life span ranging from 1.0 to 1.5 years with small L and large K values.

REFERENCES

1.

Abraham.K.J, V. S. R. Murty and K. K. Joshi, Age and growth studies in silverbellies along Kerala coast J.

Mar. Biol. Ass. India, 53 (2): 172 – 177.

2.

Bagenal, T.B. 1955. The growth rate of the long rough dab Hippoglossoides platessoides (Fabr.) J. mar. biol.

Asso. U.K.

34: 297-311.

3.

Banerji, S.K., 1973. An assessment of the exploited pelagic fisheries of the Indian seas. Proc.Symp. Living

Resources of the seas around India, Special publication, CMFRI , pp 114-136.

4.

Beverton, R.J.H. 1954. Notes on the use of theoretical models in the study of the dynamics of exploited fish populations. U.S. Fishery Lab., Misc.Contribs

., and

(2): 181, Beaufort N.Caro.

5.

Bhattacharya, C.G., 1967. A simple method of resolution of a distribution into Gaussian components.

Biometrics, 23:115-35.

6.

Chapman, D.G. and D.S.Robson, 1960. The analysis of a catch curve. Biometrics, 16 (3):354-68.

7.

Dadley, R.G., P.A.Arundhati and E.B. Brothers. 1992.

Management of the Indo-Pacific Spanish mackerel

( Scomberomorus commerson ) in Omen. Fish.Res

., 15:

17-43.

8.

Devaraj M.1982. Age and growth of three species of seer fishes Scomberomorus commerson, S. guttatus and S. lineolatus. Indian J. Fish .28 (1&2) 198:104-

127.

International Journal of Research in Fisheries and Aquaculture 2013; 3(4): 122-129

9.

Elefan 1 (Electronic Length Frequency Analysis) for estimation of growth parameters from length frequency data. ICLARM, 7 (3).

10.

FISAT. 1995. Food and Agricultural Organization

(FAO)- International Center for Living Aquatic

Resources Management (ICLARM) Stock Assessment

Tools. (Ver.1.0).

11.

Ford, E., 1933. An account of the herring investigations conducted at Plymouth during the years from 1924 to 1933. J.Mar.Biol.Assoc.U.K., 19:305-84.

12.

Gayanilo, F.C., Jr., M. Soriano and D. Pauly, 1995.

The FAO- ICLARM stock assessment tools (FISAT) user‟s guide. FAO computerised series in fisheries.

FAO, Rome, Italy.

13.

Gulland, J.A. 1969. Manual of methods for fish stock assessment. Part I. Fish population analysis . FAO

Man.Fish.Sci

., (4):154p.

14.

Gulland, J.A. and S.J. Holt, 1959. Estimation of growth parameters for data at unequal time intervals.

J.cons.CIEM

, 44:200-9.

15.

Jayabalan, N. 1991. Age and growth of the ponyfish

Secutor insidiator along PortoNovo coast. Indian J.

Mar.Sci., 20 (2): 155-156.

16.

Kasim, H.M, 1991. Shark fishery of Veraval coast with special reference to population dynamics of Scoliodon laticaudus (Muller and Henle) and Rhizoprionodon acutus (Ruppell ). J.mar.biol.Ass. India , 33 (1&2): 213-

228.

17.

Kasim, H.M, and K.M.S Ameer Hamsa and P. Sam

Bennet., 1989. Present status of perch fishery

Resources in India and its prospects. Central Marine

Fishery Research Institute Bulletin 44. Part one: 226-

237.

18.

Kasim. H.M, and T.S.Balasubramanian. 1990. Fishery, growth, yield per recruit and stock assessment of

Sphyraena obtusata (Cuvier) off Tuticorin, Gulf of

Mannar. Indian J. Fish., 37(4): 281-288.

19.

Murty, V.S. 1990. Biology and population dynamics of the silverbelly Secutor insidiator (Bloch) from

Kakinada. J.Mar.Biol.Assoc.India

. 1990. 32 (1-2): 10-

24.

20.

Pauly,D. 1985. Population dynamics of short lived species with emphasis on squids. Scientific Council

Studies No.9. Special session on Squids, September,

1984 . North West Atlantic Fisheries Organisation , pp.1-177.

21.

Pauly.D., 1980. A selection of simple methods for the assessment of tropical fish stocks . FAO Fisheries circular. No.729.FIRM

/ 129:pp54.

22.

Sekharan, K.V. 1962. On the oilsardine fishery of the

Calicut area during the years 1955-56 to 1958-59.

Indian J. Fish ., 9A (2): 679-700.

23.

Von Bertalanffy,L. 1938. A quantitative theory of organic growth. Hum. Biol ., 10: 181-213.

24.

Von Bertalanffy,L. 1934. Untersuchungen uber die

Gesetzlichkeiten des wachstums. I. Allegemeine

Grundlagen der Theorie. Roux‟ Arch. Entwick lungsmech. 131: 613-53.

25.

Walford, L.A.1946. A new graphic method of describing the growth of animals.

Biol.Bull.Mar.Biol.Lab.WoodsHole, 90: 141-7.

26.

Wetherall, J.A., J.J.Polovina and S.Ralston, 1987.

Estimating growth and mortality in steady-state fish stocks from length-frequency data. ICLARM

Conf.Proc

., (13):53-74.

27.

Yohannan, T.M. 1982. Population dynamic of Indian mackerel based on data from Mangalore during 1967-

1975. Indian J. Fish ., 29 (1&2): 50-62.

Source of support: Nil; Conflict of interest: None declared

129 International Journal of Research in Fisheries and Aquaculture 2013; 3(4): 122-129