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5. Results of the fish survey work


5.1 The echo recordings and their interpretation
5.2 The estimates of total fish biomass
5.3 Fish distribution on the Arakan Coast
5.4 Fish distribution in the Delta area
5.5 Fish distribution on the Tenasserim Coast
5.6 The distribution by depth of bottom trawl catches
5.7 The Deep Sea Shrimp Trawling Ground
5.8 Biomass estimates based on catch rates in the bottom trawl
5.9 Analysis of catches of shallow water shrimp

5.1 The echo recordings and their interpretation

Assessment of the abundance of fish resources based on acoustic observations combined with experimental fishing is a method which especially lends itself to fish found in schools or other aggregations in mid-water. This is, however, a type of behaviour which characterizes a considerable number of the fish species found in Burmese waters. But there ate also notable exceptions, e.g. surface schooling tunas and tuna-like species and strictly bottom dwelling fish such as rays and flounders. Any fish found very close to the bottom (½-1 m) or in the very surface layer will escape echo sounder detection. For navigational reasons the work with the R/V "Dr. Fridtjof Nansen" is limited to waters deeper than about 15 m. The extreme inshore waters of the northern Arakan coast, the eastern Gulf of Martaban and the mid part of the Tenasserim Coast could thus not be covered.

Because of differences in behaviour and size, different species or groups of fish species may give rise to different types of echo-recording. Small-sized pelagic fish are for instance often found in well-defined schools, the recordings of which can be distinguished from those of the often looser aggregation in which semi-demersal larger fish are often found. Such classification of the echo recordings is of considerable assistance in interpreting the acoustic observations, but a positive identification by fishing operations is still indispensable and also provides the only means of sampling fish in this type of combined survey.

Based on previous experience and on identification by fishing, the fish recordings from the Burmese waters were classified as follows:

(i) Recordings of true larger schools or dense layers mostly in upper water, Figure 11. These will most often derive from pelagic schooling fish usually of smaller size e.g. clupeiods, scads. This type was the most common in the coastal areas.

(ii) All other fish recordings which especially comprised looser agreegations of smaller and larger fish near the bottom and in mid-water. These are ascribed to demersal or semi-demersal fish such as croakers grunts, breams, snappers, sharks, ponyfish etc. This type of recording was also common, and examples are shown in Figure 12. In this group was also included single fish traces or small schools of bigger fish closer to the surface waters. These recordings are thought to derive from tunas and tuna-like fish. They were less common and probably often "lost" in dense plankton recordings near the surface.

In our analysis we will thus distinguish between the abundance and distribution of "pelagic fish" - anchovies, sardines, scads and small mackerels on the one hand and of "other fish" - croakers, grunts, snappers and other demersal and semi-demersal fish as well as larger pelagic tuna-like fish, - on the other. The catch records provide of course detailed accounts of the species caught by the various gears. One should note, however, that the terms "pelagic" and "demersal" only indicate a general tendency of behaviour. Pelagic fish are often caught in quantities in bottom trawls and pelagic trawls can be used to catch demersal fish when distributed in mid water.

Figure 11. Echo diagrams of recordings of small pelagic fish showing fish in: dense layer (upper), in small schools (middle) and in transition from dense to disperse distributions (lower)

Figure 12. Echo diagrams of recordings of "other fish" showing demersal fish, semi-demersal fish (upper and middle) and single fish traces at low speed (lower).

A third category of fish traces, i.e. from mesopelagic fish species is usually also recorded in this type of survey work. This consists of lantern fish and other small-sized related species. While found in high abundance off the shelf in the north-western Arabian Sea this type proved, however, to be relatively scarce in Burmese waters, except in a limited part of the Delta region.

The acoustic observations relating to the two categories of fish described above were recorded continuously along all survey tracks, and they form the basis for the preparation of charts of distributions of fish. The unit of measurements of fish abundance in these charts relates to the acoustic echo received from the fish and they are therefore termed echo-intensity-charts and show the relative abundance and distribution of fish. They are transferred into estimates of absolute abundance of fish biomass measured e.g. in tonnes/n.m2. by help of a conversion factor which must be adjusted to the settings and performance of the instruments and to the size of the fish in the area. The basis for this conversion is explained in Annex II to this report.

In the further descriptions of this; report the information on the distribution and behaviour of the fish obtained from the acoustic systems will be presented in the form of charts of echo-intensity distribution and will thus only show relative values. For each sub-area and category of resources a conversion to estimates of total fish biomass will be made. In addition come the catch rates and catch compositions from the fishing operations which will be used to identify, interpret and supplement the acoustic survey data.

5.2 The estimates of total fish biomass

On the basis of the charts of echo-intensity distribution the total echo- abundance for each area and type of fish was calculated by a planimetric integration. Table 2 shows the results. The table also presents the parts of the areas in which relatively dense concentrations were found. It is evident that there is a higher tendency for the small pelagic fish to be concentred in areas of higher abundance, than for the demersal and semi- demersal fish.

Table 2. Acoustic indices of abundance

SMALL PELAGIC FISH:

Indices

Dense concentrations* as % of total


Oct.-Nov.

March-April

Oct.-Nov.

March-April

Arakan coast

59.100

57.500

88

63

Delta area

103.800

219.600

50

49

Tennasserim coast

19.400

176.200

30

81

Total

182.300

453.300

60

63


OTHER FISH

Indices

Dense concentrations* as % of total


Oct.-Nov.

March-April

Oct.-Nov.

March-April

Arakan coast

21.500

19.900

32

20

Delta area

39.900

122.100

0

39

Tennasserim coast

18.400

21.900

0

0

Total

78.800

163.900

9

31

*Mean integrator values >20/n.m.
The indices of echo-abundance were then converted to estimates of biomass using the conversion factors discussed and presented in Annex II. Account should, however, be taken of the failure of the survey to cover the extreme inshore shallow water areas. These areas often hold abundant resources of fish, but in the absence of more specific information an adjustment have been made assuming that the mean fish density in the uncovered inshore areas is equal to that of the areas covered by the survey. The raising factors for the estimated total biomass are then the quotients total shelf to shelf area surveyed. They are as follows:


Autumn 1979

Spring 1980

Arakan coast

1.20

1.20

Delta area

1.44

1.16

Tennasserim coast

1.37

1.18


Table 3 shows the estimates of the biomass for the total shelf area. There is a general tendency for much higher biomass values from the spring survey than that, from the autumn. For pelagic fish the ratio is about 2, while the "other fish" biomass is increased by about 80%. The most likely explanation of this seasonal change is that it is caused by a fluctuation in biological production. Many of the fish species in this area are small-sized and have a brief life-span only. Their main period of production is adjusted to favourable ecological conditions during certain parts of the year. Similar large-scale seasonal fluctuations of the biomass of shortlived species such as sardines and anchovies have been demonstrated in nearby and comparable areas such as the coast off Pakistan and the southwest coast of India.

Table 3. Estimated biomass for the total shelf areas (In 1 000 tonnes)

SMALL PELAGIC FISH:

Area:

Autumn 1979

Spring 1980

Arakan coast

180

170

Delta area

370

640

Tennasserim coast

70

520

Total

620

1330


OTHER FISH

Area:

Autumn 1979

Spring 1980

Arakan coast

130

120

Delta area

290

710

Tennasserim coast

120

130

Total

540

960


In the following we will now consider the distribution and composition of fish biomass through a discussion of the charts of echo-abundance and of the findings of the fishing operations.

5.3 Fish distribution on the Arakan Coast


5.2.1 The small pelagic fish, Arakan coast
5.3.2 Other fish, Arakan coast
5.3.3 Results of the fishing operations, Arakan coast

The total estimated biomasses found along this part of the coast were as mentioned above as follows (1000 tons):


Autumn

Spring

Small pelagic fish

180

170

Other fish

130

120

Total

310

290


5.2.1 The small pelagic fish, Arakan coast

Figure 13 shows that the small pelagic fish are mainly distributed in the inshore areas of the coast south of Sandoway. This corresponds to the narrowest part of the shelf. Especially in the heavier concentrations the fish occuried in well defined schools during daytime as layers at night.

Aimed mid water trawling was conducted to identify these pelagic concentrations of fish.The locations of the fishing stations are shown in Figures 1-4 and the catches and their composition are recorded in Annex Table IV.The results for each of the seasons are summarized in Table 4. From this it appears that sardines and anchovies by far dominate in these catches in both seasons. In the autumn sardines occurred in 5 of 7 catches, in the spring in 7 out of 12 catches. The genera found were Sardinella, Dussumeria and Ilisha. The anchovies represented mostly by Stolephorus were almost as common as the sardines, while the remaining pelagic fish consisted of Carangids, Scomberomorus and Sphyraena. From the figures showing the mean part by weight of the catches of these various categories it is evident that the sardines anchovies and carangids generally make cut substantial parts of the catches while Scomberomorus and Sphyraena are by-catches.

(...)

Figure 13. Distribution of small "pelagic fish" on the Arakan Coast, Sep-Nov 1979 (loft), and March-April 1980 (right). For explanation of the codes for the fish names, see text.

The composition of the mid water hauls has also been used to indicate the locations of occurrence of the various types of fish in the distribution charts, Figure 13. It is, however, uncertain to which extent these indications of local occurrence provide a typical or general description of the distribution of the fish over a longer period of time.

List of codes used to indicate fish distribution in figure 13 - 18 and their corresponding fish species or group names.

Acrop

=

Acropoma japonicum

Arius

=

Arius sp.

Atrob

=

Atrobucca nibe

Car

=

Caranx sp.

Congr

=

Congresox sp.

Chrys

=

Chrysochir sp.

Decap

=

Decapterus sp.

Duss

=

Dussmeria sp.

Eng

=

Engraulis sp.

Gerr

=

Gerrus sp.

Harp

=

Harpodon sp.

Ilis

=

Ilisha

Lact

=

Lactarius lactarius

Lei

=

Leiognathus sp.

Lept

=

Lepturacanthus

Leth

=

Lethrinus sp.

Loligo

=

Loligo sp.

Nemi

=

Nemipterus

Otho

=

Otholithes sp.

Pamp

=

Pampus sp

Penna

=

Pennahia sp.

Pent

=

Pentaprion sp

Poly

=

Polynemus sp.

Pom

=

Pomadasys sp.

Rac

=

Rachycentron sp.

Rast

=

Rastrelliger sp.

Ray/ska

=

Rays and skates

Sard

=

Sardinella sp.

Saur

=

Saurida sp.

Scia

=

Scianeidae

Scomb

=

Scomberoides sp.

Selar

=

Selar sp.

Shar

=

Sharks

Shri

=

Shrimps

Sphy

=

Sphyraena sp.

Stol

=

Stolephorus sp.

Thrys

=

Thryssa sp.


The small pelagic fish also frequently occur close to the bottom especially in shallow water and are often caught in the ordinary bottom trawl. Another supplementary way then of identifying and assessing the composition of the pelagic biomass is the analysis of the occurrence of those types of fish which are known to belong to the pelagic community in all catches in the area whether from bottom or mid water trawl hauls. Table 5 shows the frequency of occurrence on the total of fishing stations for the relevant families and their proportion of the total catch of pelagic fish. The findings support those from the mid water hauls in showing the relative importance of clupeids, engraulids and carangids in a similar order. The ribbon fishes represented mainly by Lepturacanthus also make an important contribution to the pelagic biomass.

Table 5. Occurrence by families of pelagic fish on all fishing stations (bottom- and mid water trawl), and proportion by weight of total catch of pelagic fish.

ARAKAN COAST


Total no. of stations

Sept.- Nov.

March - April

56


49


No. of stations occurring

% of total catch

No. of stations occurring

% of total catch

Clupeidae

30

38

21

52

Engraulidae

22

28

12

25

Trichiuridae

20

21

14

4

Carangidae

19

3

19

16

Sphyrenidae

21

9

11

2

Scombridae

15

1

9

1


5.3.2 Other fish, Arakan coast

As shown in Figure 14 the distribution of demersal and semi-demersal fish as indicated by the acoustic data is also confined to the shelf with the centres of higher concentration well inside the shelf edge. In the March-April survey there is a tendency for this type of fish to be found even further inshore and in shallower waters than in September-October. This may be related to the lifting of the oxygen-deficient layer from autumn till spring as discussed under 4 above. An inshore movement of bottom fish may also explain the lower biomass estimate for the spring survey, a greater part of these fish is then found in the extreme inshore shallow waters which could not be covered by the survey.

Table 6 shows the occurrence of the most common families of demersal- and semi-demersal fish in the catches on the Arakan coast during the two main survey periods. Ponyfishes (Leiognatidae), croakers (Sciaenidae) and grunts (Pomadaridae) were both widespread and made out the greatest part of the catches, but also lizard fishes(Synodontidae) and catfishes (Ariidae) were common. Squids and shrimp were widespread although contributing little to the total weight of the catches in contrast to sharks and rays which made out a significant part of the catch on relatively few stations.

In the distribution maps fishes predominant in the bottom trawl hauls in the various regions have been recorded approximately where caught. In the extreme north rays and skates were found together with ponyfish, Pomadasys and Saurida. From Sandoway southwards the dominating forms are again Pomadasys and Leiognatus with Saurida, Lutjanus and Nemipterus spp.

Figure 14. Distribution of other fish on the Arakan Coast, Sep-Nov 1979 (left)and March-April 1980 (right). For explanation of the codes for the fish names, see text.

Table 6 Occurrence by families of "other fish" on all fishing stations, and their proportion by weight of total catch of "other fish".

ARAKAN COAST

Total no of stations

Sept - Nov

March-Apr

Ariidae

56

8.4

49

3.0

Carangidae

18

1.4

12

1.4

Gerridae

20

0.8

16

17.2

Lactaridae

17

5.8

10

2.1

Leiognatidae

17

7.5

9

19.0

Lutjanidae

39

1.9

19

0.6

Mullidae

14

1.1

8

2.8

Muraenesocidae

24

0.9

16

1.2

Nemipteridae

9

0.8

7

4.8

Pomadasidae

24

21.4

18

10.4

Sciaenidae

29

33.4

22

4.5

Scombridae

21

2.1

17

1.1

Synodontidae

21

1.8

13

6.2

Sharks and rays

27

3.3

26

9.6

Squids

16

0.5

8

0.8

Shrimp

28

1.4

17

2.6

Miscellaneous*

28

6.5

18

12.7

*Includes about 17 families of fish occurring in few catches, and with less than 1 % of catch and non-fish catches such as Jelly fish.

5.3.3 Results of the fishing operations, Arakan coast

A summary of all fishing activities in this area during the two periods is as follows:


BOTTOM TRAWL

PELAGIC TRAWL


Oct - Nov /79

Mar - Apr /80

Oct - Nov /79

Mar - Apr /80

Number of stations

45

28

11

22

Total catch (kg/hour units)

27420

35976

1455

5242

Mean total catch per hour kg

609

1285

132

238

Max. catch rates kg

6390

5250

380

680


The maximum catch rates shown above represent the means of the 3 highest catches.

The detailed data for each station are recorded in Annex Table IV. The average catch rate in bottom trawl in March-April/80 is about twice that in Oct-Nov/79. This should not be interpreted directly as indicating a higher abundance, since a considerable part of the autumn fishing relates to a special shrimp survey near Sandoway. Also pelagic trawling yielded somewhat higher catches during the spring survey. This may in a general way indicate a higher availability of pelagic schooling fish, but in our survey system fishing with mid-water trawl is conducted for the purpose of identifying the various types of echo-recordings of fish and for sampling and this type of operation does not provide much information of interest for assessment of fish abundance or catchability.

Bottom trawl fishing provides more comprehensive data, both with regard to the availability of the demersal stocks and the composition of the catches. One should, however, note that exploratory fishing conducted as in this survey will not simulate a commercial fishery. One important difference is that commercial fishing will be concentrated in areas with high abundance of desired species whereas the exploratory fishing will cover a wider range of fish densities. The average catch rates in this survey would thus be expected to be lower than those of a commercial fishery. There is on the other hand an effect which will act in the opposite way when the survey is conducted in an unfished virgin area. A commercial fishery will after having been established reduce the standing biomass and result in a decline of catch rates. One should keep these reservations in mind when considering the following analysis of the bottom trawl results.

Tables 7 and 8 show the distribution of the various most common forms of fish on catch groups and the mean catch. The fish forms are ranged in the order in which they contribute to the total catch. It appears that in the autumn croakers made out about 1/4 of the total catch in the area, followed by grunts and clupeoids. These three groups contributed nearly half the catch. The catch rates (standardized to one hour hauls) for each form of fish were mostly lower than 50 kg/h, but with a fair part between 50-199 kg/h and a few above 500 kg/h.

The fewer hauls in the spring were dominated by anchovies, ponyfish, mojarras and grunts with a fair number of catch rates exceeding 500 kg/h. The commercial value of the different types of fish differs considerably. To enable an evaluation on the basis of this criterion the various fish species were allocated on 4 economic classes (Appendix Table III). An analysis of the bottom trawl catches according to their composition of fish of different commercial value is shown in Table 9. It appears that more than 80% of the total catch are fish in economic class 2 and 3. The catch rates of these classes of fish (considered as a whole) are fairly high - frequently exceeding 200. kg/h and often also 500 kg/h.

Table 7. Distribution of the catches by families In 45 bottom trawl hauls on the Arakan coast Oct/Nov 1979.

Catch grouping

>10 kg/h

10-49 kg/h

50-199 kg/h

200-499 kg/h

>500 kg/h

% incidence in total no. of hauls

Mean catch

% of total catch

FAMILY:









Sciaenidae

5

8

3

0

2

40

145

24

Pomadasyidae

5

12

9

2

1

64

93

15

Clupeidae

9

9

3

0

1

49

46

8

Ariidae

9

2

1

0

1

29

37

6

Engraulidae

7

1

0

0

1

20

36

6

Trichiuridae

8

5

1

0

1

33

35

6

Leiognathidae

7

12

5

3

0

60

32

5

Lactaridae

8

6

1

0

1

36

25

4

Mesopelagic fish

0

0

1

1

0

4

12

2

Carangidae

15

8

2

0

0

56

11

2

Rays

4

1

2

1

0

18

11

2

Sphyraenidae

6

6

0

1

0

29

10

2

Scombridae

11

7

2

0

0

44

10

2

Synodontidae

13

9

1

0

0

51

8

1

Shrimps

13

7

1

0

0

47

6

1

Lutjanidae

4

7

2

0

0

29

6

1

Lobsters

3

0

1

0

0

9

3

-

Squids

14

2

0

0

0

36

2

-

Other fish







80

13

TOTAL







608

100


Table 8. Distribution of the catches by families in 28 bottom trawl hauls on the Arakan coast March/April 1980

Catch grouping

>10 kg/h


50-199 kg/h

200-499 kg/h

>500 kg/h

% incidence in total no. of hauls

Mean catch

% of total catch

FAMILY









Engraulidae

0

2

1

0

1

14

199

17

Leiognathidae

1

1

3

2

5

43

175

15

Gerridae

1

2

2

1

1

25

160

13

Pomadasyidae

3

4

8

2

1

64

95

8

Rays

3

0

2

0

2

25

89

7

Clupeidae

0

3

2

4

1

36

81

7

Synodontidae

4

7

6

0

1

64

55

5

Nemipteridae

5

6

5

0

1

61

45

4

Sciaenidae

2

7

1

3

0

46

42

4

Carangidae

2

10

2

0

1

54

37

3

Ariidae

4

2

3

1

0

36

27

2

Mullidae

6

3

4

1

0

50

26

2

Shrimps

4

8

2

1

0

54

24

2

Lactaridae

0

4

2

1

0

25

19

2

Lohsters

3

0

0

0

0

11

0.5

-

Squids

5

4

1

0

0

36

6

-

Other Fish







107

9

TOTAL







1187

100


Table 9. Distribution of the catches by economic classes in the bottom trawl on the Arakan coast.

October-November 1979

Class:

<10 kg/h

10-49 kg/h

50-199 kg/h

200-499 kg/h

>500 kg/h

% incidence in total no hauls

Mean catch

% of total catch

Economic class 1

11

21

10

2

1

84

86

14

Economic class 2

12

5

19

7

2

82

311

51

Economic class 3

11

17

11

5

1

87

193

32

Economic class 4

37

4

4

0

0

44

16

3


Birch-April 1980

Class:

<10 kg/h

10-49 kg/h

50-199 kg/h

200-499 kg/h

>500 kg/h

% incidence in total no hauls

Mean catch

% of total catch

Economic class 1

7

6

12

2

1

82

104

9

Economic class 2

5

0

8

7

8

89

494

42

Economic class 3

8

3

5

4

8

86

548

46

Economic class 4

10

10

8

0

0

79

42

3


5.4 Fish distribution in the Delta area


5.4.1 The small pelagic fish, Delta Area
5.4.2 Other fish, Delta Area
5.4.3 Results of the fishing operations, Delta area

It seems pertinent to stress that the extreme inshore parts of the Delta area particularly those of the eastern Gulf could not be covered for navigational reasons.

The total estimated biomasses during the two surveys were (in 1000 tons):


Autumn

Spring

Small pelagic fish

370

640

Other fish

290

710

Total

660

1350


5.4.1 The small pelagic fish, Delta Area

Figure 15 shows the distributions of the biomass at the two seasons. The main concentrations are found in a belt not more than about 60 n.m. wide roughly covering the bottom depth countours from about 15 to about 60-70 m.

Figure 15. Distribution of pelagic fish on the Delta Area Sep-Nov 1979) (upper) and March-April 1980 (lower), For explanations of the codes for the fish names, see text.

The biomass during the second survey (March-April) is nearly 2 times higher than that of the first, but the composition seems largely to be the same. As shown in Table 10 the most common fish in the mid water hauls were sardines, anchovies and ribbon fish. Scombrids and carangids were also relatively common. In parts of the area small pelagic shrimp (Acetes) could be found in abundance in mid water as well as on the bottom. Leiognathus, Harpodon, squid and fish larvae were also frequently found in the mid water catches.

Table 10. Identification of small pelagic fish by aimed mid water trawling. Frequency of occurrence (when being more than 10% of catch by weight) and mean part of weight of catch (%).

DELTA AREA


Sept. - Nov.

March - April

Total no. hauls

19

25

Clupeids

5 - 31 %

10 - 40 %


Sardinella

2 16 %

4 - 44 %


Ilisha

3 - 35 %

1 - 33 %


Dussumeria

1 - 16 %

4 - 14 %


Raconda


5 - 26 %

Engraulids

6 - 47 %

6 - 44 %


Thryssa

2 - 36 %

2 - 28 %


Stolephorus

4 - 53 %

4 - 43 %


Carangids

1 - 59 %

3 - 40 %


Decapterus

1 - 59 %

2 - 44 %

Scombrids

6 - 25 %

4 - 41 %


Scomberomorus

4 - 27 %

3 - 36 %


Rastrelliger

2 - 16 %


Trichiurids

8 - 28 %

12 - 26 %


Lepturacanthus

6 - 25 %

12 - 26 %

Leiognatus

5 - 43 %

5 - 74 %

Shrimp

4 - 38 %

2 - 16 %

Miscellaneous

9 - 39 %

13 - 38 %


Judging from the occurrence in all catches with both mid water and bottom trawls, the ribbon fishes seem to have the widest and highest abundance followed by engraulids and clupeids, see Table 11. Carangids, scombrids and sphyraenids also occur frequently, but make out a much smaller part of the total catch of pelagic fish.

Table 11, Occurrence by families of pelagic fish on all fishing stations (bottom- and mid water trawl), and proportion by weight of total catch of pelagic fish.

DELTA AREA

Total no of stations

Sept - Nov

March - April

70


95


No of stations occurring

% of total catch

No if stations occurring

% of total catch

Clupeidae

31

11

33

24

Engraulidae

34

35

44

33

Trichiuridae

44

40

55

35

Carangidae

23

6

29

7

Sphyrenidae

12

7

10

1

Scombridae

12

2

5

1


5.4.2 Other fish, Delta Area

The oceanographical regime which no doubt governs the distribution of bottom fish in this area is related to the river outflows and there is as demonstrated in chapter 4 above a marked change in both salinity- and temperature conditions from September-November till March-April. The change in the distribution of the fish with considerably higher concentrations during the last cruise may well be related to the change of the environment.

In the central and eastern parts of the Delta area some difficulties of identification of the echo recordings were encountered with relation to the occurrence both in mid water and closer to the bottom of shrimp of the Genus Acetes which is of little or no commercial interest. Relatively heavy concentrations of mesopelagic fish located in the southern part of the central Delta area are not included in the fish distribution chart.

Table 12 shows the occurrence in the catches of the most common forms of fish during the two surveys. The relatively high abundance of croaker (Sciaenidae) and catfishes (Ariidae) is a common feature with the fauna of the Arakan coast, but otherwise the Delta fauna differs in several respects from those of the coastal regions to the north and south. Noteworthy is the regular presence of threadfins (Polynemidae), pike congers (Muraenesocidae;) and Bombay duck (Harpodontidae). Sharks and rays are (...) widespread and abundant, while ponyfish (Leiognathus) is far less common than in the other areas.

Figure 16. Distribution of other fish on the Delta Area Sep-Nov 1979 (upper) and March-April 1980 (lower). For explanation of the codes for the fish names, see text.

The prominent forms in the catches are roughly located in Figure 16. Rays and skates are common everywhere while Polynemus is found in the central and eastern parts. Harpodon is particularly dominant in the catches from the shallow eastern parts of the Delta. Saurida and Nemipterus are common in the southeast towards the Tenasserim coast.

Table 12. Ocurence by families of "other fish " on all fishing stations and their proportion by weight of the total catch of "other fish"

DELTA AREA

Total no of stations

Sept - Nov

March - Apr

No of stations occurring

% of total catch

No of stations occurring

% of total catch

Ariidae

70

4.4

95

8.1

Carangidae

29

0.2

36

6.1

Gerridae

8

1.3

27

1.0

Harpadontidae

18

2.2

10

20.5

Lactaridae

8

2.1

18

1.6

Letognatidae

11

2.6

21

1.3

Lutjanidae

25

4.2

26

2.6

Mullidae

22

1.9

20

3.3

Muraenesocidae

24

5.6

23

1.4

Nemipteridae

20

2.6

19

2.9

Polynemidae

26

6.2

21

3.0

Pomadasidae

19

0.9

25

2.7

Sciaenidae

28

18.5

26

9.7

Scombridae

33

2.2

37

0.8

Synodontidae

16

2.8

20

2.4

Sharks and rays

20

18.3

24

13.9

Squids

53

0.8

52

0.6

Shrimp

23

11.6

27

6.9

Miscellaneous

40

11.2*

40

12.0

*include 12 families of the fish occurring in few catches and with less than of catch

5.4.3 Results of the fishing operations, Delta area

A summary of all fishing stations in this area during the two periods is as follows:



BOTTOM TRAWL

PELAGIC TRAWL

Sept - Nov /79 Mar - Apr / 80

Sept - Nov / 79 Mar - Apr / 80

Number of stations

44

57

26

39

Total catch (kg)

18280

29248

6021

21786

Mean total catch per hour (kg)

415

513

232

559

Max. catch rates (kg/h)

2260

1380

1140

5340


Some of the bottom trawling in the spring formed part of a special trawl survey of the eastern Delta to obtain an independent estimate of demersal fish and especially the stock of Bombay duck. The mid water hauls may be interpreted as an indication of increased availability from autumn to spring of small pelagic fish. The maximum catch rates represent the mean of the three highest catches.

Tables 13 and 14 show the distribution on catch groups and mean catch rates for the most common types of fish. The largest parts of the total catch were made out of few forms: croakers, rays, ponyfish, pike congers, threadfins, Bombay ducks and ribbonfish. These types also gave the highest catches although the overall means are only of the order of 30-70 kg/h. A special survey was as already mentioned made of the Bombay duck-distribution which accounts for the relatively high values in the spring.

Table 13. Distribution of the catches by families in 44 bottom trawl hauls in the Delta area Oct/Nov 1979

Catch grouping

>10 kg/h

10-49 kg/h

50-199 kg/h

200-499 kg/h

>500 kg/h

incidence in total no of hauls

Mean catch

% of total catch

FAMILY









Sciaenidae

17

10

15

1

1

68

71

18

Rays

25

8

8

2

1

52

47

12

Shrimps

19

16

7

2

0

70

37

9

Polynemidae

34

3

6

1

0

39

24

6

Muraenesocidae

26

11

7

0

0

43

22

6

Trichiuridae

36

14

3

1

0

43

22

5

Ariidae

25

15

4

0

0

66

17

4

Lutjanidae

32

10

1

1

0

43

16

4

Sharks

31

12

0

1

0

52

14

3

Synodontidae

2

11

0

1

0

41

11

3

Engraulidae

34

9

1

0

0

48

8

2

Nemipteridae

31

11

2

0

0

50

10

3

Sphyraenidae

40

1

0

1

0

14

7

2

Mullidae

34

9

1

0

0

48

7

2

Lactaridae

42

1

0

1

0

11

7

2

Leiognathidae

36

6

2

0

0

34

7

2

Harpadontidae

38

3

3

0

0

16

6

2

Carangidae

37

6

1

0

0

30

5

1

Gerreidae

36

7

0

0

0

36

5

1

Clupeidae

38

5

1

0

0

41

5

1

Other fish







50

12

TOTAL







398

100


Table 14. Distribution of the catches by families in 57 bottom trawl hauls on the Delta area March/April 1980

Catch grouping

>10 kg/h

10-49 kg/h

50-199 kg/h

200-499 kg/h

>500 kg/h

% incidence in total no of hauls

Mean catch

% of total catch

FAMILY









Harpadontidae

43

4

2

3

5

28

87

17

Rays

35

7

12

1

2

47

52

10

Scianidae

26

16

14

1

0

60

40

8

Leiognatidae

44

4

6

2

1

30

36

7

Ariidae

29

19

7

1

1

63

30

6

Engraulidae

40

7

8

2

0

54

26

5

Shrimps

45

10

2

0

0

40

25

5

Trichiuridae

36

13

7

1

0

60

22

4

Carangidae

42

10

4

1

0

42

17

3

Mullidae

44

10

2

1

0

35

14

3

Clupeidae

46

7

3

1

0

37

13

3

Nemipteridae

40

13

4

0

0

35

12

2

Polynemidae

47

7

2

1

0

39

12

2

Mesopelagic fish

56

0

0

0

1

2

12

2

Pomadasyidae

39

14

4

0

0

40

11

2

Synodontidae

42

13

2

0

0

33

10

2

Lutjanidae

50

6

0

1

0

30

8

2

Sharks

45

10

2

0

0

40

7

1

Lactaridae

53

2

2

0

0

18

6

1

Lethiridae

54

2

0

1

0

7

6

1

Serranidae

54

2

0

1

0

11

6

1

Muraenescidae

47

9

1

0

0

29

5

1

Acropomidae

55

1

0

1

0

7

5

1

Other fish







52

10

TOTAL






57

514

99


Table 15 Distribution of the catches by economic classes in, the bottom trawl on the Delta area.

October-November 1979

Class:

<10 kg/h

10-49 kg/h

50-199 kg/h

200-499 kg/h

>500 kg/h

% incidence in total no of hauls

Mean catch

% of total catch

Economic class 1

4

13

20

5

2

98

116

29

Economic class 2

2

12

25

4

1

100

120

30

Economic class 3

3

12

18

9

2

100

138

34

Economic class 4

20

18

5

1

0

86

26

7


March-April 1980

Class:

<10 kg/h

10-49 kg/h

50-199 kg/

200-499 kg/h

>500 kg/h

% incidence in total no of hauls

Mean catch

% of total catch

Economic class 1

7

20

23

6

1

98

94

18

Economic class 2

10

16

16

15

0

89

109

21

Economic class 3

9

4

20

12

12

95

272

53

Economic class 4

20

30

6

0

1

89

40

8


The analysis of the catches from a point of view of commercial value, Table 15 shows that the fish of the Delta area tends to be of higher economic value than was the case for the Arakan coast with 20-30% of the catch being referred to the highest value class. The mean catch rate in this class is of the order of 100 kg/h, but there are single catches exceeding 500 kg/h.

5.5 Fish distribution on the Tenasserim Coast


5.5.1 The small pelagic fish on the Tenasserim coast
5.5.2 Other fish on the Tennasserim coast
5.5.3 Results of the fishing operations, Tenasserim Coast

The total estimated biomasses were (1000 tons):


Autumn

Spring

Small pelagic fish

70

520

Other fish

120

130

Total

190

650


The coverage during the second survey included more of the inshore waters of the southern archipelago, but this can not explain the great difference in the findings since most of the fish occurred in the areas covered by both surveys.

5.5.1 The small pelagic fish on the Tenasserim coast

The biomass of the second survey is some 7 times that of the first. The distributions are shown in Figure 17. From the mid water trawling it is evident that anchovies represented by far the most widely distributed and common fish, see Table 16. But also sardines were wide-spread, while scombrids and carangids were only found in 4 out of 20 hauls in the spring cruise.

The analysis of the total fishing stations, presented in Table 17, indicate a wide distribution by area of both anchovies and sardines, but a marked dominance in catches of anchovy. Also the other pelagic fish families are shown to have a relatively wide distribution, but with small total catches compared to that for anchovy.

The areas of high abundance during the second survey formed a belt some 20 n.m. wide in the waters of the archipelago. The boundaries of these fish areas towards the shallower inshore waters were located except in the region from abt. 11°50' to 12°30' LN where inshore navigation was not possible.

Figure 17. Distribution of small pelagic fish on the Tennasserim coast Sep-Nov 1979 (left) and March-April 1930 (right). For explanation of the codes for the fish names, see text.

5.5.2 Other fish on the Tennasserim coast

The densities of demersal and semi-demersal fish are considerably lower on the Tenasserim coast than in the Delta area and also significantly below those of the Arakan coast which represent a much smaller shelf area. There are no marked differences in distributional features between the two surveys as seen in Figure 18.

Table16. Identifications of small pelagic fish by aimed mid water trawling. Frequency of occurrence (when more than 10 % by weight) and mean proportion of weight catch (%).

TENASSERIM COAST


Sept.-Nov.

March - April

Total no. Hauls

4

20

Clupeids


7 - 33 %


Ilisha

2 - 16 %

4 - 22 %


Dussumeria


5 - 13 %

Engraulids

3 - 16 %



Stolephorus

2 - 24 %

14 - 70 %


Thryssa

1 - 11 %


Scombroids


4 - 36 %


Scomberomorus


2 - 57 %


Rastrelliger

1 31 %

2 - 15 %

Carangids


4 - 37 %


Decapterus

1 - 10 %

2 - 46 %


Selar


2 - 27 %

Trichiurids




Lepturacanthus

1 - 16 %

2 - 34 %

Sphyrena

1 - 17 %

2 - 21 %

Leiognatus

1 - 25 %

2 - 24 %

Miscellaneous

1 - 78 %

3 - 25 %


Table 17. Occurrence by families of pelagic fish on all fishing stations (bottom- and mid water trawl), and proportion by weight of total catch of pelagic fish.

TENASSERIM COAST

Total no of stations

Sept. - Nov.

March - April

23


57


No. of stations occurring

% of total catch

No. of stations occurring

% of total catch

Clupeidae

8

1

26

14

Engraulidae

9

92

22

74

Trichiuridae

11

1

14

4

Carangidae

13

1

24

5

Sphyrenidae

7

3

15

1

Scombridae

4

1

15

1


Table 18 shows the occurence in the catches of the most common forms of fish. Ponyfishes (Leiognathidae), grunts (Pomadasyidae), lizardfishes (Synodontidae), and false trevallies (Lactarida) are widespread and relatively abundant. The high percentage of ponyfish in the March-April survey is caused by some exceptionally high catches in shallow waters. More characteristic for the area is perhaps the relatively frequent occurrence of threadfin breams (Nemipteridae) and goatfishes (Mullidae). Squids are widespread, but represent a small part of the catch, while sharks and rays are far less common than in the two northern areas.

Table 18. Occurrence by families of "other fish" on all fishing stations, and their proportion by weight of the total catch of "other fish"

TENNASSERIM COAST

Total no of stations

Sept - Nov

March - Apr

No of stations occurring

% of total catch

No of stations occurring

% of total catch

Ariidae

23

2.7

57

5.4

Carangidae

8

2.1

12

2.3

Gerridae

6

2.1

15

1.3

Lactaridae

10

12.0

11

4.0

Leiognatidae

6

15.5

11

56.9

Lutjanidae

14

1.7

24

2.9

Mullidae

88

4.8

10

2.7

Muraenesocidae

10

3.5

22

0.5

Nemipteridae

8

4.7

5

2.0

Pomadasidae

11

6.4

21

6.5

Sciaenidae

9

12.7

18

0.9

Synodontidae

8

2.6

9

3.6

Sharks and rays

10

3.1

19

0.8

Squids

10

1.9

8

0.6

Shrimps

10

2.5

23

0.3

Miscellaneous

6

21.7

8

9.3


The forms dominating the catches in the various locations are shown in Figure 18. Leiognathus has generally the most inshore distribution while Nemipterus, Saurida, Atrobucca, Lutjanus and Loligo are prominent in the more offshore parts of the archipelago.

5.5.3 Results of the fishing operations, Tenasserim Coast

A summary of the fishing stations in this area during the two periods is as follows:



BOTTOM TRAWL

PELAGIC TRAWL

Sep - Nov /79 Mar - Apr /80

Sep - Nov / 79 Mar - Apr /80

Number of stations

16

26

7

30

Total catch (kg)

14308

27074

579

8923

Mean total catch per hour (kg)

894

1041

83

297

Max. catch rates (kg /h)

3930

5070

510

1060


Figure 18. Distribution of other fish on the Tennasserim Coast Sep-Nov 1979 (left) and March-April 1980 (right). For explanation of the codes for the fish names, see text.

The fishing was considerably less intensive than in the-two other areas. The higher catches in the pelagic trawl in the spring support the impression of a higher total biomass of small pelagic fish in this season.

Table 19. Distribution of the catches by families in 16 bottom trawl hauls on the Tennasserim coast Oct/Nov 1979

Catch grouping

>10 kg/h

10-49 kg/h

50-199 kg/h

200-499 kg/h

>500 kg/h

% incidence in total no of hauls

Mean catch

% of total catch

FAMILY









Engraulidae

13

1

1

0

1

19

577

68

Sciaenidae

12

0

4

0

0

44

33

4

Leiognathidae

7

5

4

0

0

63

32

4

Lactaridae

15

0

0

1

0

19

31

4

Pomadasyidae

9

6

1

0

0

56

17

2

Mullidae

13

4

1

0

0

56

12

1

Nemipteridae

10

5

1

0

0

63

12

1

Carangidae

9

7

0

0

0

63

12

1

Trichiuridae

12

3

1

0

0

50

9

1

Muraenesocidae

14

0

2

0

0

19

9

1

Clupeidae

14

1

1

0

0

25

9

1

Other fish







99

12

TOTAL







852

100


The catch distributions are shown in Tables 19 and 20. The dominance of anchovy in the autumn data is caused by one large catch. The spring survey probably gives a better picture of the composition of the bottom fish in the area and the catch rates for the various forms. Ponyfish contributed some high catches, but otherwise the mean catch rates of croakers, cat-fishes and carangids were about the same as in the Delta area.

Table 20. Distribution of the catches by families in 26 bottom trawl hauls on the Tennasserim coast March - April 1980

Catch grouping

>10 kg/h

10-49 kg/h

50-199 kg/h

200-499 kg/h

>500 kg/h

% incidence in total no of hauls

Mean catch

% of total catch

FAMILY









Leiognathidae

13

1

3

3

6

58

510

49

Sciaenidae

18

3

2

2

1

35

81

8

Pomadasyidae

12

6

6

2

0

69

59

6

Ariidae

18

2

3

3

0

42

49

5

Carangidae

18

7

5

1

0

73

37

4

Lactaridae

17

4

4

1

0

38

36

3

Synodontidae

19

3

8

0

0

62

32

3

Clupeidae

18

6

3

1

0

50

31

3

Lutjanidae

20

3

2

1

0

31

25

2

Mullidae

16

5

5

0

0

73

24

2

Nemipteridae

16

13

3

0

0

73

18

2

Engraulidae

23

2

0

1

0

15

15

1

Gerreidae

23

2

0

1

0

35

11

1

Trichiuridae

22

2

2

0

´

19

11

1

Other fish







104

10

TOTAL







1048

100


The commercial value of the bottom fish on the Tennasserim coast appears, however, as seen in Table 21, to be much lower in general than that of the more northern parts with a dominance of fish of economic class 3.

Table 21 Distribution of the catches by economic classes in the bottom trawl on the Tennasserim coast

October -November 1979


>10 kg/h

10-49 kg/h

50-199 kg/h

200-499 kg/h

>500 kg/h

% incidence in total no of hauls

Mean catch

% of total catch

Economic class 1

5

6

5

0

0

88

43

5

Economic class 2

5

2

8

1

0

88

95

11

Economic class 3

3

4

7

1

1

88

671

79

Economic class 4

9

2

4

1

0

81

44

5


March April 1980


>10 kg/h

10-49 kg/h

50-199 kg/h

200-499 kg/h

>500 kg/h

% incidence in total no of hauls

Mean catch

% of total catch

Economic class 1

2

9

12

3

0

100

95

9

Economic class 2

2

6

8

6

4

96

270

26

Economic class 3

7

3

6

2

9

77

636

61

Economic class 4

8

12

5

1

0

96

43

4


5.6 The distribution by depth of bottom trawl catches

Table 22 shows an analysis of catch rates versus depth, and their composition by economic classes. On the Arakan coast the catch rates in the shallowest zone 10-24 m is clearly higher in the spring than in the autumn. This is probably related to the change in the oceanographical conditions between the two seasons as discussed in chapter 4. In the spring, water with low oxygen content, cover large areas of the shelf and will cause A shoreward movement of the demersal fish. Fishing at depths greater than 50 m gave low catch rates on the Arakan coast, but the economic value of the catch in deeper waters was relatively higher than at shallower depths.

In the Delta there is no clear seasonal difference in the depth distribution of the catches and the catch rates decline more slowly with depth although there is a clear tendency for highest rates in depths of less than 50 m. The value of the fish is relatively higher in the deeper strata. On the Tennasserim coast the relatively few hauls indicate high catch rates in the shallowest strata dominated by fish of economic class 3 (ponyfish), with lower catch rates but relatively more valuable fish in the deeper waters.

Table 22. Mean catch in bottom trawl by depth strata and by economic classes (kg/h).

ARAKAN COAST


Dept in metres

SPRING

10-24

25-49

50-74

75-149

Economic class 1:

98

141

2

0

Economic class 2:

482

357

22

0

Economic class 3:

869

737

2

0

Economic class 4:

43

49

13

0

Economic class 1 - 4:

1492

1284

39

0

Number of hauls:

11

13

4

0

AUTUMN:





Economic class 1:

127

109

33

72

Economic class 2:

181

572

27

42

Economic class 3:

115

342

21

15

Economic class 4:

6

9

2

26

Economic class 1 - 4:

429

1032

83

155

Number of hauls:

8

21

5

5

DELTA AREA





SPRING:





Economic class 1:

93

77

137

27

Economic class 2:

84

231

49

46

Economic class 3:

329

308

37

3

Economic class 4:

24

15

146

34

Economic class 1 - 4:

530

631

369

110

Number of hauls:

35

12

8

3

AUTUMN:





Economic class 1:

219

101

144

34

Economic class 2:

135

187

65

43

Economic class 3:

177

212

83

35

Economic class 4:

34

10

11

16

Economic class 1 - 4:

565

510

303

128

Number of hauls:

7

17

10

7

TENNASSERIM COAST





SPRING:





Economic class 1:

102

92

41

135

Economic class 2:

359

360

124

10

Economic class 3:

851

907

185

7

Economic class 4:

39

59

54

11

Economic class 1 - 4:

1351

1417

404

163

Number of hauls:

10

8

4

4

AUTUMN:





Economic class 1:

83

40

33

30

Economic class 2:

144

75

107

100

Economic class 3:

3284

115

40

17

Economic class 4:

172

4

26

29

Economic class 1 - 4:

3681

234

206

176

Number of hauls:

3

6

4

2


5.7 The Deep Sea Shrimp Trawling Ground

Along the Arakan coast and down to about 13ºLat.N the slope of the shelf beyond one hundred fathoms is very steep and generally unsuitable for trawling. In the Andaman Sea from 13ºLat.N southwards to about 10ºLat.N the shelf edge which here lies some 100 n.m. offshore is far less abrupt and slopes only gently down towards a steep fall-off beyond 500 m's depth. There is thus formed a very extensive ground some 200 n.m. long and from abt 10-40 n.m. wide with predominantly even ground suitable for bottom trawling. The ambient conditions on this ground with temperatures of 11-12ºC and oxygen content of abt 0.8 ml/l are similar to those found within the same depth ranges off the SW Indian coast and off Sri Lanka in the Gulf of Mannar. In these other locations deep sea shrimp and -lobsterhave been found to exist partly in commercial quantities together with various species of deep sea fish.

Figure 19. Trawl stations on the Deep Sea Trawling Ground

Exploratory fishing was carried out on this deep sea ground both in October-November and in March-April. A total of 38 hauls were made with the ordinary shrimp-cum fish trawl equipped with bobbins. Figure 8 shows the locations of the fishing stations set out in a map where also the contours of the 200, 300, 400 and 500 m depth are shown. Table 23 presents a summary of the findings.

Table 23. Catch rates at the Deep Sea Trawling Ground (kgs/h).



No hauls

Total catch

Shrimps

Lobster

Fish

Range

Mean

Range

Mean

Range

Mean

Range

Mean

Oct - Nov 1979

20

40-176

178

0-155

34

0-28

4

40-450

140

March - April 1980

18

76-328

133

0-65

18

0-36

7

46-300

108


The shrimp species were Heterocarpus sp., Aristaeus semidentatus and others. The lobster represents the species Puerulus sewelli. The most common deep sea fish in the catches were: Peristedion weberi, Chloropthalmus sp. and Palinurichtus pringlei.

The catch rates obtained in this exploration are far too low to be of commercial interest. In a similar survey in the Gulf of Mannar off Sri Lanka catch rates ranged up to abt 500 kg/hour for shrimp, 140 kg/hour for deep sea lobster and 1.2 tons/hour for fish. The total area of the deep water ground in the Andaman Sea is, however, very extensive and the resources of shrimp, lobster and deep sea fish must be very considerable in terms of total biomass. Some further trial fishing should be conducted to see whether there exist seasons or areas of higher concentrations than those found during the present survey.

5.8 Biomass estimates based on catch rates in the bottom trawl

The bottom trawl fishing was in general not distributed in a manner which allows an analysis of the catches for quantitative estimates of the biomass.

In a few areas the trawl survey approximated, however, a fixed grid system. Nakken and Sann Aung (1980) reported on the results of an analysis of such data from the autumn survey. In April a trawl survey was conducted of the eastern shallow part of the Delta area in which the location was chosen on a grid basis, see Figure 4. The data were as follows:

No of trawl stations:

21

Mean catch per n.m.:

209 kg

SD

141 kg


If the trawl width is taken as 18.5 m (0.01 n.m.), the trawled area per nautical mile will be 0.01 n.m2. If the catchability coefficient is assumed to be l i.e, all fish in front of the trawl opening is caught, 209 kg/n.m. will correspond to a fish density of about 21 / tons n.m2. The area covered was approximately 6 000 n.m.2, which would then hold an estimated biomass of 126 000 tons. An estimate of the biomass of demersal and semi-demersal fish based on the acoustic observations within this area gives a figure which exceeds 300 000 tons. This represents, however, the biomass of fish classified as "other fish" in the total water column from about 10 m under the surface to the bottom, whereas the trawl will only catch fish closer than 5 m from the bottom.

In part of the area covered by the trawl-survey Bombay duck was abundant. In 9 hauls the catches of this species ranged from 0 - 390 kg/n.m. with an average of 157 kg/n.m., corresponding to a density of 15.7 tons/n.m.2. The estimated biomass in a 2 700 n.m.2 - area was thus about 42 000 tons.

5.9 Analysis of catches of shallow water shrimp

The survey tasks did not include that of the assessing the resources of shallow water shrimp which is of such considerable commercial importance in Burma. A shrimp survey would have required different types of gear, vessel and survey design. However, shrimp formed part of the catch in a number of the trawl hauls especially in shallow waters in the Delta and on the Arakan coast, and an analysis of the shrimp data was made as follows:

In order to limit the study to areas where shrimp is reasonably abundant only trawl hauls with catches of shrimp exceeding 10 kg/h were considered. Furthermore the analysis was limited to Penaeid shrimp by excluding "small shrimp" or "white shrimp", mainly Acetes spp. with no commercial value. The results of the analysis are shown in Table 24. The mean catch rates were 28 kg/h and 60 kg/h on the Arakan coast in autumn and spring respectively and 73 kg/h and 65 kg/h in the Delta in the two seasons. The fish catch was on the average very high in these hauls with shrimp only forming between 1 and 13 percent of the total catches. Metapenaeus dominated the catches with Penaeus as the second most important genus. An analysis of the depth distribution of the catches indicated that by far the highest rates were obtained in the 10-24 m stratum. The rates decreased to about 1/4 in the 25-49 m depth stratum on the Arakan coast. The decline of catch rates with depth was even more pronounced in the Delta, but shrimp occured even to depths beyond 75 m in this region although in small numbers.

Table 24. Analysis of catches of shrimp in bottom trawl.



ARAKAN

DELTA

TENNASSERIM

Oct - Nov 79

Mar - Apr 80

Oct - Nov 79

Mar - Apr 80

Oct - Nov 79

Mar - Apr 80

Total no of hauls

45

28

77

57

16

26

No of hauls with catch >10 kg/h of shrimps*

8

10

10

12

0

1

Mean catch/hour shrimps* (kg)

28

60

73

65


12

Mean bycatch of fish in hauls of shrimps >10 kg/h*

2284

1890

480

698


376

Mean bycatch of fish in %

998

97

87

91


97

Composition of the catches (%) and no of stations with catch of shrimps >10 kg/h (in brackets)*








Metapenaeus lyssianasa



50 (3)





Metapenaeus sp

(2)

67 (6)

29 (6)

91 (11)




Parapenaeopsis sculptilis




9 (1)




Penaeus merguiensis


12 (2)

3 (1)





Panaeus monodon

(1)

21 (3)

8 (3)



100 (1)


Solenocera sp



10 (2)





Unidentified

(5)






* Excluding all records classified as "shrimps" in the record, if the weight is not >10 g/specimen. "small shrimps " are mainly Acetes sp.


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