Scottish Marine and Freshwater Science Volume 6 Number 3: Effects of Codend Mesh Size and Twine Number on Nephrops Selectivity: Report of Fishing Industry Science Alliance (FISA) Project 03/13
A set of trials were conducted in the West Coast to examine the selectivity of nephrops (Nephrops norvegicus) with regards to codends of differing mesh sizes and construction.
Appendix: Tables and Figures
Note: for the relative catch rate figures below a solid line denotes where the catch rate is significantly different from 100 %. A broken line shows where the rate is not significantly different.
Figure 1. Comparison of raised nephrops length frequency for the control net (white bars) and the three test nets (black bars). Results are amalgamations of all hauls for the particular test case.
Figure 2. The relative catch rate of nephrops by codend from smoothed data.
Figure 3. Haddock - top row: combined number caught v length by the control (white bars) and test nets (black bars). Bottom row: focus on the numbers from the test net.
Figure 4. The relative catch rate of haddock by codend from smoothed data. Note that in the case of the 120 mm codend the analysis shows that the trend with length continues and that for haddock >30 cm the relative catch rate is not significantly different from the control net, however, this is not illustrated here.
Figure 5. Whiting - top row: combined number caught v length by the control (white bars) and test nets (black bars). Bottom row: focus on the numbers from the test net.
Figure 6. The relative catch rate of whiting by codend from smoothed data
Figure 7. Plaice combined numbers caught at length by the control nets (white bars) in comparison to the test nets (black bars).
Figure 8. The relative catch rate of plaice for 100 mm codend from smoothed data.
Figure 9. Witch: combined numbers caught at length by the control nets (white bars) in comparison to the test nets (black bars).
Figure 10. The relative catch rate of witch for 100 mm codend from smoothed data.
Figure 11. Lemon sole: combined numbers caught at length by the control nets (white bars) in comparison to the test nets (black bars).
Figure 12. Hake: combined numbers caught at length by the control nets (white bars) in comparison to the test nets (black bars).
Figure 13. Bottom: approximate percentage 'fate at length' of commercially caught nephrops from the North and South Minch (source: MSS observer data 2013). Fates are illustrated as a percentage of three available to each mm carapace length grouping - light grey area: discarded, dark grey area: landed as tails, cross-hatched area: landed as whole. Top: relative catch rates of the 3 test gears as Figure 2 which can be applied to each length/fate. The length range illustrated is the same as that analysed during these trials.
Percentage fates as illustrated represent an amalgamation of observer data covering both the North and South Minch during all 4 quarters of 2013 and incorporate information from both 80 mm and 100 mm codends. The figure, then, should not be taken as definitive but as a guide. As in other areas market forces, seasonal forces, working logistics and individual vessel practice all heavily influence the patterns of tailing and landing of whole nephrops in the Scottish west coast fishery.
Figure 14. Approximate midpoints (open circles) of hauls undertaken during the trials.
Table 1. Weight (kg) of Nephrops, haddock, whiting, other commercial species (others 1), non-commercial species and invertebrates (others 2) by haul number and test configuration (mesh size and whether fished port or starboard on the twin-rig). Missing haul numbers refer to foul hauls.
Haul no. | Test Config | Control Net | Test Net | % bulk Wt. reduction |
||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Nephrops | Haddock | Whiting | others 1 | others 2 | Totals | Nephrops | Haddock | Whiting | others 1 | others 2 | Totals | |||
1 | 80 Stbd | 39.8 | 14.7 | 7.5 | 0.2 | 50 | 112 | 35.1 | 13.5 | 3.9 | 1.9 | 26 | 80 | 28 |
2 | 80 Stbd | 127.2 | 62.8 | 11.0 | 4.7 | 124 | 330 | 92.7 | 21.6 | 5.4 | 10.4 | 93 | 223 | 32 |
3 | 80 Stbd | 59.9 | 12.4 | 1.0 | 3.5 | 105 | 182 | 56.2 | 8.1 | 1.4 | 6.5 | 65 | 137 | 25 |
5 | 120 Stbd | 136.5 | 53.6 | 8.6 | 3.7 | 44 | 246 | 61.3 | 2.7 | 0.5 | 4.7 | 13 | 82 | 67 |
6 | 120 Stbd | 115.6 | 30.4 | 10.6 | 6.3 | 61 | 224 | 44.5 | 1.7 | 0.9 | 2.8 | 32 | 82 | 63 |
7 | 120 Stbd | 126.1 | 24.8 | 6.4 | 6.0 | 72 | 235 | 39.6 | 1.9 | 0.2 | 0.8 | 34 | 76 | 68 |
8 | 100 Stbd | 96.3 | 94.3 | 29.8 | 6.7 | 58 | 285 | 78.0 | 15.3 | 2.2 | 5.7 | 14 | 115 | 60 |
9 | 100 Stbd | 151.1 | 83.4 | 33.0 | 10.2 | 107 | 385 | 122.8 | 8.1 | 2.4 | 5.4 | 25 | 164 | 57 |
10 | 100 Stbd | 123.7 | 14.2 | 5.1 | 4.9 | 74 | 222 | 67.1 | 6.4 | 0.1 | 6.4 | 18 | 98 | 56 |
11 | 100 Stbd | 55.6 | 14.4 | 4.5 | 8.1 | 205 | 288 | 26.4 | 10.2 | 2.5 | 5.9 | 126 | 171 | 41 |
12 | 100 Port | 59.4 | 78.9 | 1.1 | 3.2 | 47 | 190 | 31.2 | 51.1 | 0.4 | 2.1 | 29 | 114 | 40 |
13 | 100 Port | 26.4 | 80.1 | 0.7 | 2.1 | 66 | 175 | 11.8 | 33.9 | 0.7 | 3.0 | 25 | 74 | 58 |
14 | 100 Port | 178.6 | 38.7 | 8.3 | 10.3 | 74 | 310 | 92.3 | 5.5 | 1.4 | 3.8 | 15 | 118 | 62 |
15 | 80 Port | 89.2 | 35.6 | 7.2 | 3.7 | 98 | 234 | 63.1 | 6.4 | 5.8 | 4.2 | 15 | 94 | 60 |
16 | 80 Port | 53.1 | 27.4 | 5.7 | 1.8 | 79 | 167 | 38.4 | 3.0 | 2.5 | 4.8 | 21 | 70 | 58 |
17 | 80 Port | 54.0 | 44.3 | 6.8 | 2.7 | 103 | 211 | 33.5 | 13.6 | 2.3 | 4.1 | 17 | 71 | 67 |
18 | 80 Port | 136.8 | 85.7 | 2.0 | 3.7 | 81 | 309 | 102.0 | 2.8 | 1.1 | 2.6 | 16 | 124 | 60 |
19 | 80 Port | 203.0 | 30.2 | 5.9 | 9.4 | 79 | 327 | 133.5 | 1.8 | 1.3 | 8.8 | 31 | 176 | 46 |
20 | 80 Port | 73.6 | 30.6 | 3.4 | 6.6 | 89 | 203 | 58.1 | 2.4 | 1.4 | 6.2 | 17 | 85 | 58 |
21 | 80 Port | 100.0 | 28.3 | 5.0 | 7.4 | 52 | 193 | 75.2 | 1.4 | 0.2 | 1.1 | 33 | 111 | 42 |
23 | 100 Port | 73.0 | 27.5 | 5.8 | 3.5 | 43 | 153 | 55.1 | 1.3 | 0.1 | 3.2 | 5 | 65 | 58 |
24 | 100 Port | 136.0 | 33.0 | 4.9 | 3.3 | 72 | 249 | 70.0 | 1.8 | 0.3 | 1.5 | 8 | 82 | 67 |
25 | 100 Port | 88.2 | 37.0 | 6.8 | 7.0 | 86 | 225 | 50.7 | 2.1 | 0.8 | 3.0 | 11 | 68 | 70 |
26 | 120 Port | 44.0 | 9.7 | 0.3 | 5.2 | 101 | 160 | 21.4 | 9.7 | 0.0 | 2.5 | 24 | 58 | 64 |
27 | 120 Port | 58.0 | 27.5 | 1.0 | 2.9 | 67 | 156 | 23.5 | 16.0 | 0.9 | 1.4 | 19 | 61 | 61 |
28 | 120 Port | 58.3 | 11.9 | 4.9 | 2.8 | 74 | 152 | 25.9 | 7.4 | 0.2 | 1.6 | 22 | 57 | 62 |
29 | 120 Port | 91.2 | 6.8 | 17.4 | 30.8 | 60 | 206 | 39.8 | 0.6 | 1.0 | 6.0 | 10 | 57 | 72 |
30 | 120 Port | 60.3 | 1.6 | 5.3 | 9.1 | 38 | 114 | 28.3 | 0.0 | 0.9 | 11.3 | 11 | 52 | 55 |
31 | 120 Port | 79.6 | 10.8 | 14.2 | 68.7 | 41 | 214 | 37.9 | 1.6 | 2.4 | 62.9 | 11 | 116 | 46 |
32 | 120 Port | 88.6 | 9.4 | 10.7 | 16.3 | 40 | 165 | 42.3 | 4.1 | 3.4 | 34.9 | 25 | 110 | 33 |
33 | 100 Stbd | 78.2 | 13.5 | 35.8 | 8.5 | 62 | 198 | 69.3 | 5.6 | 3.5 | 6.6 | 32 | 117 | 41 |
34 | 100 Stbd | 63.9 | 9.3 | 12.8 | 14.5 | 91 | 191 | 48.9 | 5.0 | 3.2 | 8.0 | 44 | 109 | 43 |
35 | 100 Stbd | 110.8 | 10.1 | 5.6 | 26.5 | 99 | 252 | 86.7 | 2.7 | 1.8 | 7.6 | 49 | 148 | 41 |
36 | 100 Stbd | 85.6 | 6.7 | 10.0 | 45.6 | 149 | 297 | 64.8 | 3.0 | 0.7 | 13.6 | 30 | 112 | 62 |
37 | 120 Stbd | 157.8 | 51.4 | 11.0 | 7.6 | 120 | 348 | 81.7 | 0.8 | 0.5 | 3.2 | 5 | 91 | 74 |
38 | 120 Stbd | 67.4 | 50.5 | 50.4 | 10.4 | 112 | 291 | 36.1 | 1.8 | 0.5 | 2.0 | 52 | 92 | 68 |
39 | 120 Stbd | 94.1 | 47.4 | 21.6 | 4.9 | 329 | 497 | 68.1 | 19.9 | 3.7 | 3.1 | 72 | 167 | 66 |
40 | 120 Stbd | 154.8 | 40.4 | 23.2 | 4.6 | 343 | 566 | 73.8 | 16.1 | 7.3 | 3.9 | 52 | 153 | 73 |
41 | 80 Stbd | 132.7 | 23.1 | 7.2 | 6.1 | 430 | 599 | 137.6 | 4.4 | 1.8 | 9.4 | 53 | 206 | 66 |
42 | 80 Stbd | 85.9 | 52.5 | 24.7 | 4.7 | 340 | 508 | 73.9 | 1.8 | 2.5 | 3.3 | 27 | 108 | 79 |
43 | 80 Stbd | 44.6 | 54.6 | 17.5 | 1.4 | 318 | 436 | 46.6 | 4.6 | 1.5 | 1.2 | 26 | 80 | 82 |
Table 2. Retention (% by weight) for the three main commercial species caught. It is important to note that these retention values will apply only to the length frequencies encountered (as illustrated in Figures 1, 3 and 5).
Haul | 80mm | Haul | 100mm | Haul | 120mm | ||||||
---|---|---|---|---|---|---|---|---|---|---|---|
Nephrops | Haddock | Whiting | Nephrops | Haddock | Whiting | Nephrops | Haddock | Whiting | |||
1 | 88 | 92 | 52 | 8 | 81 | 16 | 7 | 5 | 45 | 5 | 6 |
2 | 73 | 34 | 49 | 9 | 81 | 10 | 7 | 6 | 38 | 5 | 8 |
3 | 94 | 65 | 146 | 10 | 54 | 45 | 3 | 7 | 31 | 8 | 4 |
15 | 71 | 18 | 80 | 11 | 47 | 71 | 55 | 26 | 49 | 100 | 0 |
16 | 72 | 11 | 44 | 12 | 53 | 65 | 37 | 27 | 41 | 58 | 89 |
17 | 62 | 31 | 34 | 13 | 45 | 42 | 89 | 28 | 44 | 62 | 4 |
18 | 75 | 3 | 54 | 14 | 52 | 14 | 16 | 29 | 44 | 9 | 6 |
19 | 66 | 6 | 22 | 23 | 75 | 5 | 1 | 30 | 47 | 1 | 16 |
20 | 79 | 8 | 41 | 24 | 51 | 5 | 6 | 31 | 48 | 15 | 17 |
21 | 75 | 5 | 5 | 25 | 57 | 6 | 12 | 32 | 48 | 44 | 32 |
41 | 104 | 19 | 26 | 33 | 89 | 42 | 10 | 37 | 52 | 2 | 5 |
42 | 86 | 3 | 10 | 34 | 77 | 54 | 25 | 38 | 54 | 3 | 1 |
43 | 104 | 8 | 8 | 35 | 78 | 27 | 31 | 39 | 72 | 42 | 17 |
36 | 76 | 45 | 6 | 40 | 48 | 40 | 31 | ||||
Overall | 79 | 17 | 30 | Overall | 67 | 22 | 12 | Overall | 47 | 20 | 12 |
Table 3. Mean wingspreads (m) by haul. Missing values refer to periods of no data. Missing haul numbers refer to foul hauls.
Haul no. | wing spreads | Haul | wing spreads | ||
---|---|---|---|---|---|
Port | Stbd | no. | Port | Stbd | |
1 | - | - | 24 | - | - |
2 | - | - | 25 | 8.4 | 8.6 |
3 | - | - | 26 | - | 9.4 |
5 | 8.4 | 8.7 | 27 | 8.1 | 8.6 |
6 | 8.1 | 8.1 | 28 | - | 8.2 |
7 | - | 8.6 | 29 | 8.5 | 8.6 |
8 | 8.2 | 9.9 | 30 | 8.9 | 8.7 |
9 | 8.0 | 8.0 | 31 | 8.6 | 8.5 |
10 | - | 8.5 | 32 | 8.8 | 8.4 |
11 | - | 7.6 | 33 | 8.7 | - |
12 | 8.6 | - | 34 | 8.5 | 9.1 |
13 | 8.4 | 8.4 | 35 | 8.3 | 8.6 |
14 | 8.2 | 8.4 | 36 | 9.2 | 8.8 |
15 | 8.1 | 8.5 | 37 | 8.3 | 8.4 |
16 | 8.6 | 8.5 | 38 | 8.2 | 8.4 |
17 | 8.8 | 8.6 | 39 | - | 7.6 |
18 | 8.5 | 9.4 | 40 | 8.5 | 7.9 |
19 | 8.6 | 8.4 | 41 | - | - |
20 | 8.0 | 8.2 | 42 | 8.8 | 8.0 |
21 | 8.0 | 8.2 | 43 | 8.7 | 8.2 |
23 | - | - |
mean overall wingspreads: Port - 8.4 Stbd - 8.5
Table 4. P-values: pairwise comparisons between test gears and control. Shaded areas indicate significant difference (P<0.05).
Species | Window | Half-Range | Test Gear | 80mm | 100mm | 120mm | control |
---|---|---|---|---|---|---|---|
Nephrops | 21 | 19.5 - 54.5 | 80mm | - | 0.022 | 0.000 | 0.000 |
100mm | - | - | 0.000 | 0.000 | |||
120mm | - | - | - | 0.000 | |||
Haddock | 9 | 8.5 - 25.5 | 80mm | - | 0.569 | 0.012 | 0.000 |
100mm | - | - | 0.022 | 0.000 | |||
120mm | - | - | - | 0.000 | |||
Whiting | 13 | 9.5 - 32.5 | 80mm | - | 0.024 | 0.000 | 0.000 |
100mm | - | - | 0.004 | 0.000 | |||
120mm | - | - | - | 0.000 | |||
Plaice | 9 | 16.5 - 30.5 | 100mm | - | - | - | 0.000 |
Witch | 15 | 13.5 - 30.5 | 100mm | - | - | - | 0.000 |
Table 5. Test codend makeup. All codends and straight sections were constructed from Brezline ( PE).
Test mesh (nominal) | Approx. mesh size pre-Trial |
% > nominal size |
Codend twine number and thickness |
Codend no. meshes deep |
Codend approx. length |
Straight section twine number and thickness |
Overall Length |
No. open meshes across |
---|---|---|---|---|---|---|---|---|
80 | 83 | 3.8 % | 4mm single 80mm | - | - | 4mm single 80mm | 12m | 51 |
100 | 104 | 4.0 % | 5mm double 100mm | 50 | 5m | 5mm single 100mm | 12m | 44 |
120 | 124 | 3.3 % | 5mm double 120mm | 50 | 6m | 5mm single 120mmm | 12m | 44 |
Table 6. Mean codend mesh measurements (30 measurements on each of top and bottom sheet over the area of selectivity during the trials). All measurements were taken with a standard Omega gauge on wet meshes.
mesh | pre-trials mean size |
post-trials mean size |
---|---|---|
80mm | 82.7 | 81.8 |
100mm | 103.8 | 102.4 |
120mm | 123.9 | 122.0 |
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