566 Square-mesh codend circumference and selectivity Matt K. Broadhurst and Russell B. Millar Broadhurst, M. K., and Millar, R. B. 2009. Square-mesh codend circumference and selectivity. – ICES Journal of Marine Science, 66: 566 –572. Despite the wide-scale assessment and the use of square-mesh codends in demersal trawls, relatively few studies have tested the effects of configurations other than mesh size on their selectivity. We investigated the consequences of increasing the circumference of square-mesh codends used in an Australian penaeid fishery from the expected optimal configuration of 33% of maximum diamond-mesh extension to 56 and 75%. Three square-mesh designs comprised 27-mm polyamide mesh throughout and had the same length (100 bars, B), but different circumferences (90, 150, and 200 B, respectively). Paired simultaneous comparisons (using twin trawls) of each treatment codend against a small-meshed control revealed significant effects of circumference on the efficiency of the trawl for a small teleost (pink-breasted siphonfish, Siphamia roseigaster) and commercial size classes of school prawns (Metapenaeus macleayi). Compared with the 90 codend, pink-breasted siphonfish catches and prawn count (numbers per 500 g) were both significantly greater in the codends of larger circumference, and these effects are attributed to concomitant (i) convoluted or reduced lateral openings of meshes and (ii) lesser probabilities of organisms encountering meshes in the posterior section. These differences would not preclude the use of codends of larger circumference in the fishery, but they do highlight the need to select appropriate configurations in future studies to reduce the potential for including the confounding effects of different geometries. Keywords: bycatch, fishing gear technology, gear selectivity, penaeids. Received 12 June 2008; accepted 31 December 2008; advance access publication 3 February 2009. M. K. Broadhurst: NSW Department of Primary Industries, Fisheries Conservation Technology Unit, PO Box J321, Coffs Harbour NSW 2450, Australia. R. B. Millar: Department of Statistics, The University of Auckland, Private Bag 92019, Auckland, New Zealand. Correspondence to M. K. Broadhurst: tel: þ61 2 6648 3905; fax: þ61 2 6651 6580; e-mail: mbroadhurst@nmsc.edu.au. Introduction Demersal otter trawls are used throughout the world and account for almost a quarter of the global landed marine catch (estimated at 86 million tonnes in 2004; Kelleher, 2005; FAO, 2007). Otter trawls retain disproportionately large ratios of incidental (i.e. bycatch) to targeted catches (for reviews, see Andrew and Pepperell, 1992; Kelleher, 2005), because of their active fishing mechanisms, the frequent use of small diamond-shaped mesh and, for penaeid trawls, deployment across nearshore habitats characterized by abundant assemblages of small species. Although the overall design of a trawl influences the type and quantity of catch that enters the gear, it is generally accepted that beyond this point, selection is largely determined by (i) the lateral mesh openings in the codend, and (ii) the probability that these are encountered (MacLennan, 1992; Wileman et al., 1996). An obvious prerequisite towards achieving desired selection in otter trawls is to regulate a suitable mesh size in the codend, although this is not the only determining factor. Other parameters known to influence diamond-shaped mesh openings in codends include twine diameter (Sala et al., 2007) and material (Tokaç et al., 2004), length of the extension section (Reeves et al., 1992), towing speed (Dahm et al., 2002), catch weight (Campos et al., 2003), presence of codend attachments (Kynoch et al., 2004) or restrictions (Lök et al., 1997), and codend circumference (Reeves et al., 1992; Broadhurst and Kennelly, 1996; Lök et al., 1997). Of these factors, the last is among the most important and has been identified in several studies as having a strong negative relationship with selectivity that can be explained by an associated reduction in lateral mesh openings as the surface area of the netting increases (Reeves et al., 1992; Broadhurst and Kennelly, 1996). One simple modification to maintain openings in codends is to orientate the meshes on the bar so that they are square-shaped (Robertson, 1986). Often, compared with diamond-mesh codends, those made from mesh of similar or even smaller size hung on the bar have increased 50% size-at-retention (L50) and/or reduced selection range (SR) for a variety of species (Robertson and Stewart, 1988; Halliday and Cooper, 2000; Broadhurst et al., 2004; Bahamon et al., 2006). Although square-mesh codends maintain consistently wider openings than diamond-mesh designs, they are still characterized by variability in performance, which might be attributed to the confounding effects of at least some of the factors listed above (Halliday and Cooper, 2000; Campos et al., 2003; Bahamon et al., 2006; Macbeth et al., 2007). For example, Campos et al. (2003) and Macbeth et al. (2007) observed positive relationships between catch weights in square-mesh codends and the L50 of blue whiting (Micromesistius poutassou) and the SR of school prawns (Metapenaeus macleayi), respectively. Further, Halliday and Cooper (2000) suggested that, as for diamond mesh (e.g. Tokaç et al., 2004), square-mesh codends made from polyamide (PA) twine could provide higher values of L50 than those constructed of polyethylene (PE) twine. The circumference of square-mesh codends has also been implicated as impacting on selection, but like other parameters, the magnitudes of such effects are less clear than for diamond mesh (Broadhurst et al., 1999a, 2004). Specifically, Robertson (1986) # 2009 International Council for the Exploration of the Sea. Published by Oxford Journals. All rights reserved. For Permissions, please email: journals.permissions@oxfordjournals.org 567 Square-mesh codend circumference and selectivity suggested that if square-mesh codends were constructed with circumferences considerably larger than the expected fishing circumference of the anterior diamond-mesh extension section, their meshes could convolute, so reducing and/or masking lateral openings. Similarly, during work to examine two square-mesh codends in a southern Australian penaeid-trawl fishery, Broadhurst et al. (1999a) observed a greater L50 and lower SR for western king prawns (Penaeus latisulcatus) in a tapered and slightly narrower design, possibly because of an increased encounter probability with the mesh, i.e. (ii) above. The same trend was not evident for comparable square-mesh designs tested in a different fishery, but this was partially attributed to the attachment of a novel release mechanism that reduced available mesh openings, irrespective of circumference (Broadhurst et al., 2004). Despite the potential for some confounding effects of circumference, most studies that have compared diamond- and squaremesh codends have ignored the issue. This is demonstrated in several cases where, apart from the mesh size, no technical specifications on square-mesh designs were provided (Petrakis and Stergiou, 1997; Ordines et al., 2006). In other studies where such information is available, there is variability among relative circumferences, which can be illustrated by calculating the maximum circumference of the square-mesh codend as a proportion of the theoretical maximum, i.e. the mesh size times the number of meshes around, of the conventional diamond-mesh design or extension section. Such proportions typically range from 0.3 (Campos et al., 2003; Bahamon et al., 2006; Macbeth et al., 2007) to 0.5 (Robertson and Stewart, 1988; Halliday and Cooper, 2000). It remains unclear to what extent, if any, such differences among relative circumferences would have on the selectivity or efficiency of square-mesh codends. We examined this relationship in the New South Wales (NSW) river penaeid trawl fishery, which consists of up to 204 small vessels (,10 m) targeting mainly school prawns (but also catching some eastern king prawns, Penaeus plebejus) at three locations (the Clarence, Hunter, and Hawkesbury rivers). During the past 20 years, concerns over large bycatches of nontarget, economically important species by these trawlers culminated in the development and legislation of a range of bycatch reduction devices, such as the Nordmøre-grid, in the trawl extension section, followed more recently by codends made from 27-mm PA mesh (2.25 m diameter, ø, twine) hung on the bar to replace conventional 40-mm diamond-mesh designs (Macbeth et al., 2007). The 27-mm mesh was chosen to select school prawns at industry-preferred categories of between 150 and 180 individuals 500 g – 1. Here, all mesh sizes refer to mesh opening according to Ferro and Xu (1996). Based on the fishing circumference of the anterior extension section (and corresponding to the area of the Nordmøregrid—400 600 mm) of the gear used by NSW river trawlers, the optimal circumference of the 27-mm square-mesh codend was calculated as 1.4 m or 90 B (Figure 1; Robertson, 1986; Broadhurst et al., 2004). Although Macbeth et al. (2007) demonstrated that this codend selected school prawns at appropriate sizes across a range of trawlers and conditions, some fishers suggested that larger circumferences would be beneficial for accommodating greater catch volumes. Given the above, our aims were to examine the effects on catches associated with increasing the circumference from 90 (1.4 m) to 150 (2.4 m) and 200 B (3.2 m); corresponding to relative increases from 0.33 to 0.56 and 0.75 of the maximum circumference of the extension section. Figure 1. Schematic diagram of the penaeid trawl, with the Nordmøre-grid and 90 codend attached. PE, polyethylene; PA, polyamide; N, normals; B, bars; ø, diameter. 568 Material and methods Equipment used The experiment was carried out on commercial trawl grounds for penaeids in Lake Wooloweyah (part of the Clarence River system, 298260 S 1538220 E), NSW, during October and November 2007. A local trawler towing two Florida Flyer trawls (each with a headline length of 7.32 m) in a conventional twin-gear configuration was chartered to conduct the research. Both trawls contained aluminium Nordmøre-grids with bar spaces of 20 mm, located in an extension section made from 40-mm PE mesh and with a circumference of 100 meshes in the transverse (T) direction (Figure 1). Zippers (Buraschi S 146R, 1.45 m long) were secured posterior to the Nordmøre-grids to facilitate changing the codends (Figure 1). One control and three treatment square-mesh codends were constructed for use with the trawls. All codends were made from dark knotless polyamide mesh netting and had a length of 1.58 m. The three treatment designs (termed the 90, 150, and 200 codends) consisted of 27-mm mesh (2.25 mm ø braided twine) hung on the bar and had the same length (100 B; Figure 1), but different circumferences, 90, 150, and 200 B, respectively. The 90 codend had a maximum circumference of 1.42 m (i.e. 90 15.75 mm centre bar to centre bar), the same as the estimated fishing circumference of the diamond-mesh extension section (i.e. 100 T a fractional mesh opening of 0.3 40-mm mesh and accounting for a twine diameter, ø, of 2 mm). The control codend was made from 9-mm (1.5-mm ø braided twine) mesh hung on the bar and measured 386 263 B. To maintain symmetry, all codends were constructed in two sections, each section consisting of upper and lower panels sewn together in opposite directions (see Broadhurst et al., 2004, for details of their construction). Zippers (see above) were attached to the anterior sections of each codend to allow attachment to the trawl extension section. Experimental design and analyses Between 07:00 and 14:00 on each day of fishing, the three treatment codends were compared with the control in independent, paired 40-min deployments across a combination of sandy and mud substrata in depths ranging from 1 to 2 m. Two replicate deployments of each treatment codend against the control were made each day, providing a total of 18 deployments for each comparison over 9 d. The daily order of the deployments was randomized within complete blocks, so that one deployment of all three treatments against the control was completed before starting the second replicate for each treatment. After each deployment, the two codends being examined were emptied onto a partitioned tray. Catches were separated by species and the following categories of data collected on board for each codend: the weights of total penaeids and bycatch; the numbers of all species comprising bycatch; and the total lengths (TLs in mm) of pink-breasted siphonfish (Siphamia roseigaster, the only teleost caught in sufficient numbers with sizes small enough to pass through the square meshes). Random samples of 1 kg of penaeids from each codend were placed into plastic bags and processed in the laboratory. During this latter work, all individuals were separated by species. The data collected from each sample included carapace lengths (CL in mm) and weights of all eastern king prawns and 250 school prawns (from a random subsample). These data were then used to calculate the numbers and weights of M. K. Broadhurst and R. B. Millar total school and eastern king prawns in each deployment, and the industry size category of the number of school prawns 500 g21. For the two penaeid species and pink-breasted siphonfish caught in the three experimental gears, logistic and Richard’s selection curves were obtained via the SELECT method (Millar and Walsh, 1992) by fitting a single combined curve to the collection of size frequency datasets from the individual deployments, as described in Millar et al. (2004). This provides an estimate of overdispersion to adjust estimated standard errors so that they incorporate the effects of between-haul variability and the subsampling of catches. The bivariate form of Wald’s F-test (applied to the L50 and SR parameter estimates) was used to test for significant differences between pairs of gears (Kotz et al., 1982). In addition to pairwise tests, the hypothesis that all three codends were identical was tested simultaneously. Millar et al. (2004) cautioned that the combined curve fits may not be reliable for multiple gear comparisons when using conventional techniques such as parametric likelihood ratio tests. Instead, a permutation test was used with the likelihood ratio as the test statistic, so avoiding the need to make parametric assumptions about the distribution of the likelihood ratio test statistic. Under the null hypothesis, all 54 deployments (i.e. 18 for each of the three treatments and their controls) have the same selection curve. This null hypothesis was tested under two scenarios: (i) individually varying the relative fishing efficiencies of each deployment; and (ii) a common relative efficiency. Under the first scenario, the null hypothesis is that the selection curves of the three gears are identical, whereas under the second scenario, the null hypothesis is that the selection curves and relative efficiency of the three gears are identical (Millar and Fryer, 1999). In all, 1000 permutations were done for each test, and all the analyses were done using the freely available R language. Analysis of variance (ANOVA) was used to investigate the hypothesis of no differences among catches (numbers and weights) of the three treatment codends. Data for those variables that were present in sufficient numbers were ln(x þ 1) transformed (to account for multiplicativity) and used (after preliminary tests for heteroscedasticity) in balanced two-factor ANOVA (with codends and days considered fixed and random factors, respectively). Results In all, 88 272 organisms, comprising 23 species, were retained by the three treatment codends, although most of the catches by number were school prawns (85%), followed by eastern king prawns (12%). Bycatches consisted of one crustacean and 20 teleost species and were dominated by pink-breasted siphonfish (1.1% of the total catch by number), silver biddy (Gerres subfaciatus, 1.1%), Ramsey’s perchlet (Ambassis marianus, 0.5%), and southern herring (Herklotsichthys castelnaui, 0.4%). Of the species caught, only eastern king (6–27 mm CL) and school prawns (5 –24 mm CL) and pink-breasted siphonfish (30–65 mm TL) were small enough to escape through the codend meshes. All remaining abundant teleosts ranged from 70 to 250 mm TL. The species compositions and the mean (+s.e.) catches of targeted penaeids (4.87 + 0.25 kg) and bycatch (0.37 + 0.06 kg) per 40-min deployment were consistent with those typically experienced in the fishery. 569 Square-mesh codend circumference and selectivity Size selection Richard’s and logistic selection curves were converged for school and eastern king prawns and pink-breasted siphonfish, but based on the inspection of residuals and tests of deviance, the latter models were preferred (Figure 2, Table 1). Owing to low catches of pink-breasted siphonfish in the 90 codend, it was necessary to fix the value of the relative fishing efficiency parameter, P, because it could not be estimated reliably. The value used was P ¼ 0.67, corresponding to the average of the estimated values of P for the 150 and 200 codends (Table 1). Fixing P precluded any variance estimates for the parameter vectors or subsequent Table 1. Lengths in mm and (s.e.) at 50% probability of retention (L50), SR, and relative fishing efficiencies (P) for school prawns (Metapenaeus macleayi), eastern king prawns (Penaeus plebejus), and pink-breasted siphonfish (Siphamia roseigaster) from the 90, 150, and 200 codends. Parameter 90 codend L50 SR P School prawns Eastern king prawns Pink-breasted siphonfish 10.97 (0.34) 4.51 (0.72) 0.48 (0.01) 12.94 (1.86) 7.19 (3.06) 0.54 (0.06) 150 codend L50 SR P 10.41 (0.22) 2.67 (0.42) 0.51 (0.01) 9.63 (0.85) 3.37 (1.86) 0.47 (0.02) 58.93 (7.92) 9.28 (2.44) 0.69 (0.25) 200 codend L50 SR P 10.57 (0.23) 2.89 (0.42) 0.49 (0.01) 11.97 (0.84) 4.34 (1.72) 0.52 (0.04) 57.24 (7.31) 9.22 (2.98) 0.65 (0.22) 82.98 23.10 0.67 pairwise tests for these data, but they were still amenable to the permutation tests, because of the absence of distributional assumptions. For all three species, the estimated L50s and SRs of the 90 codend were larger than those of both the 150 and 200 codends (Figure 2, Table 1). However, bivariate Wald tests failed to detect any significant differences among appropriate pairwise comparisons (p-values ranged between 0.08 and 0.94). Note that there were seven pairwise tests (because only the 150 vs. 200 comparison was made for pink-breasted siphonfish), and using the Bonferonni correction, a significance of 0.05/7 0.007 would be required to reject the null hypothesis, but the smallest observed p-value was 0.08 for school prawns between the 90 and 150 codends. The permutational test of the hypothesis that the selection curves were identical provided similar conclusions to the Wald tests for all three species (p . 0.05). However, when the assumption of identical relative efficiency was added to the analyses, and using a Bonferonni adjusted significance level of 0.05/6 0.008 for the total of six permutation tests employed, the null hypothesis of same selection curve and relative efficiency was not rejected for eastern king and school prawns (p . 0.008), but it was rejected for pink-breasted siphonfish (p , 0.001). Species selection Figure 2. Logistic selection curves for (a) school prawns (Metapenaeus macleayi), (b) eastern king prawns (Penaeus plebejus), and (c) pink-breasted siphonfish (Siphamia roseigaster). The shaded areas encompass relevant size frequency data from the control codend. There were no significant interactions between square-mesh codends and days in the ANOVA models applied to the variables examined (p . 0.05). Further, except for the number of southern herring, all interactions had p-values of .0.25, so this term was pooled with the residual to increase the power for the main effects of days and the key factor of interest, codends. All variables, except for the number of southern herring, returned significant main effects of days (p , 0.05). There were no significant differences among codends for the weights and numbers of total penaeids (F2,43 ¼ 0.30 and 1.17, p . 0.05), school prawns (F2,43 ¼ 0.30 and 0.91, p . 0.05), or eastern king prawns (F2,43 ¼ 0.49 and 0.29, p . 0.05), or for the weight of bycatch (F2,43 ¼ 0.18, p . 0.05) and the numbers of silver biddy (F2,43 ¼ 0.30, p . 0.05), southern herring (F2,16 ¼ 0.53, p . 0.05), and Ramsey’s perchlet (F2,43 ¼ 0.64, p . 0.05; 570 M. K. Broadhurst and R. B. Millar Figure 3. Barplots of mean catch (þs.e.) in the 90, 150, and 200 codends for the weights of (a) total penaeids, (b) school prawns (Metapenaeus macleayi), (c) eastern king prawns (Penaeus plebejus), and (d) bycatch, and the numbers of (e) total penaeids, (f) school prawns, (g) eastern king prawns, (h) school prawns per 500 g, (i) pink-breasted siphonfish (Siphamia roseigaster), (j) silver biddy (Gerres subfaciatus), (k) southern herring (Herklotsichthys castelnaui), and (l) Ramsey’s perchlet (Ambassis marianus). Black barplots represent significant F-ratios. Figure 3a–g, j –l). However, compared with the 90 codend, the means of these penaeid and teleost variables were greater and less, respectively, in the codends of larger circumference (Figure 3a–g, j– l). Significant differences were detected among codends for the numbers of school prawns per 500 g (F2, 43 ¼ 5.86, p , 0.01) and pink-breasted siphonfish (F2, 43 ¼ 5.51, p , 0.01), with fewer catches in the 90 codend than in the larger circumference designs (Figure 3 h and i). Discussion The estimated selectivity parameters for school prawns for each of the three square-mesh codends were within the range provided by Macbeth et al. (2007) for the recommended, smallestcircumference design tested on ten trawlers throughout the NSW river fishery. Although this result further supports the broad utility of square mesh for consistently selecting penaeids of appropriate size across a range of configurations and fishing conditions (Broadhurst et al., 1999a; 2004), the potential nevertheless exists for at least some confounding effects of circumference, manifest here as significant differences among codends for the number of school prawns per 500 g and their relative efficiencies for pink-breasted siphonfish. These differences can be explained with respect to species morphology and the possible changes to codend mesh geometry associated with increasing circumference. Specifically, at an optimal configuration, the maximum lateral and diagonal openings of the square-shaped 27-mm mesh were 13.5 and 19.1 mm, respectively. Based on morphological relationships calculated by Dingle (2008), pink-breasted siphonfish at 50 mm TL (a typical size in the catch) have a height and width of 13.4 and 5.9 mm, so any fish of this size or smaller that were swimming in the codends and encountered meshes should have been able to pass through, irrespective of their perpendicular orientation. Further, even the largest pink-breasted siphonfish (65 mm TL) recorded in the treatment codends had a maximum height of ,19 mm and could have penetrated the meshes by orientating obliquely. This clearly occurred at a significantly and incrementally greater rate in the conventional 90 codend than in the 150 and 200 codends, which may be indicative of at least two possible concomitant departures from optimal mesh geometry in the latter designs. First, increasing the codend circumference beyond that of the extension section in the 150 and 200 codends would have created surplus netting during fishing, with convoluted and/or narrower, more rectangular openings (Robertson, 1986), especially in the anterior sections close to where the circumference was physically maintained at 1.4 m by the Nordmøre-grid (Figure 1). Even a slight departure from the optimal square shape would reduce the escape of the larger pink-breasted siphonfish with heights close to the maximum mesh opening. Second, the codends of larger circumference would have allowed the catch to spread more laterally, possibly increasing the diameter of their posterior sections (Broadhurst et al., 1999b). Any pink-breasted siphonfish swimming immediately in front of the build-up of catch in the 150 and 200 codends would have had to travel greater distances towards the netting than in the 90 codend and, therefore, may have had a lesser probability of encountering openings. Either of these effects could account for the significant two- and threefold increases in the numbers of pink-breasted siphonfish retained in the 150 and 200 codends. 571 Square-mesh codend circumference and selectivity The significantly fewer school prawns per 500 g and the nonsignificant, but nevertheless, slightly greater selectivity parameters and lower catches of both penaeids in the 90 codend compared with the two larger-circumference designs support the above geometry-related impacts, though at reduced magnitudes. Such relatively milder impacts on penaeids may reflect known differences in their morphology and behaviour. Like pink-breasted siphonfish, most eastern king and school prawns, i.e. ,20 mm CL, had carapace heights and widths that were less than the maximum lateral mesh opening (13.5 mm; Dingle, 2008). Unlike pink-breasted siphonfish, however, both penaeids are characterized by considerable morphological discontinuities and appendages, which probably restricted their passage through the meshes more than codend geometry. Further, penaeids and crustaceans in general are known to exhibit quite different behavioural responses to trawl-induced stimuli than fish, which typically include fewer active attempts at penetration through codend meshes (Watson, 1989). In addition to the significant direct impacts of codend circumference on school prawns and pink-breasted siphonfish, there was some evidence of indirect contrary effects on the other teleosts caught in sufficient quantities for meaningful analyses, including silver biddy, southern herring, and Ramsey’s perchlet. All three species are laterally compressed and were caught at sizes (.70 mm TL) with corresponding heights well more than the maximum mesh opening (Dingle, 2008). Such morphology effectively precluded their escape through any of the codend meshes, so their catches would not be expected to vary with circumference. However, although not significant, there were fewer of these fish in the codends of larger circumference, opposite to the situation observed for pink-breasted siphonfish. One explanation for this anomaly is that greater drag attributable to the additional netting material and lateral distribution of the catch in the larger-circumference codends increased the displacement of water forwards (Broadhurst et al., 1999b) and assisted some larger silver biddy, southern herring, and Ramsey’s perchlet to swim out through the escape exit at the top of Nordmøre-grid (Figure 1). Broadhurst and Kennelly (1996) attributed similar flow-related effects of circumference in diamondmesh codends to a significant increase in the escape of fish of comparable size through a strategically located square-mesh panel. As the swimming speed of fish is a positive function of their size (Beamish, 1978), such effects may not have extended to the much smaller pink-breasted siphonfish. Notwithstanding the significant confounding effects of codend circumference observed in this study, the magnitudes of differences for school prawns and the low overall quantities of small teleosts (such as pink-breasted siphonfish) likely to be selected out of the mesh would not preclude NSW river trawlers from using circumferences of up to 3.2 m. Nevertheless, these results still have implications for other trawl fisheries where the quantities of bycatches are much greater, and particularly those characterized by large numbers of fish with transverse morphologies similar to the mesh openings. Considering the observations here for pinkbreasted siphonfish, even a slight increase in the circumference of square-mesh codends from 0.33 to 0.56 of the maximum circumference of the extension section has the potential to result in twice as many of these small animals being retained. Conversely, if the trends observed here for the relatively larger silver biddy, southern herring, and Ramsey’s perchlet are maintained, then any increases in the codend circumference in penaeid trawls might be offset by a greater escape of fish through strategic, anterior escape openings (Broadhurst and Kennelly, 1996). Given the results of this study, future research may benefit from a closer examination of the influence of the circumference of square-mesh codends on their performance. The same logic would also extend to other variables that are also likely to influence selection, including twine diameter and material (Halliday and Cooper, 2000; Sala et al., 2007). Isolating any confounding effects of these parameters could facilitate a clearer evaluation of the underlying effects of the mesh size and shape and, ultimately, the design of optimal configurations. Acknowledgements The work was funded by the NSW Department of Primary Industries. Shane McGrath, Craig Brand, Stephan Soule, and the Clarence River commercial fishers are thanked for their assistance. References Andrew, N. L., and Pepperell, J. G. 1992. The by-catch of shrimp trawl fisheries. Oceanography and Marine Biology: an Annual Review, 30: 527– 565. Bahamon, N., Sardà, F., and Suuronen, P. 2006. Improvement of trawl selectivity in the NW Mediterranean demersal trawl fishery by using a 40 mm square mesh codend. Fisheries Research, 81: 15– 25. Beamish, F. W. H. 1978. Swimming capacity. In Fish Physiology. 7. Locomotion, pp. 101 – 187. Ed. by W. S. Hoar, and D. J. Randall. Academic Press, New York. Broadhurst, M. K., and Kennelly, S. J. 1996. Effects of the circumference of codends and a new design of square-mesh panel in reducing unwanted by-catch in the New South Wales oceanic prawn-trawl fishery, Australia. Fisheries Research, 27: 203– 214. Broadhurst, M. K., Kennelly, S. J., and Eayrs, S. 1999b. Flow-related effects in prawn-trawl codends: potential for increasing the escape of unwanted fish through square-mesh panels. Fishery Bulletin US, 97: 1 – 8. Broadhurst, M. K., Larsen, R. B., Kennelly, S. J., and McShane, P. E. 1999a. Use and success of composite square-mesh codends in improving size-selectivity of prawns in Gulf St Vincent, South Australia. Fishery Bulletin US, 97: 434– 448. Broadhurst, M. K., Millar, R. B., Kennelly, S. J., Macbeth, W. G., Young, D. J., and Gray, C. A. 2004. Selectivity of conventional diamond- and novel square-mesh codends in an Australian estuarine penaeid-trawl fishery. Fisheries Research, 67: 183– 194. Campos, A., Fonseca, P., and Erzini, K. 2003. Size selectivity of diamond and square mesh cod ends for four by-catch species in the crustacean fishery off the Portuguese south coast. Fisheries Research, 60: 79– 97. Dahm, E., Wienbeck, H., West, C. W., Valdemarsen, J. W., and O’Neill, F. G. 2002. On the influence of towing speed and gear size on the selective properties of bottom trawls. Fisheries Research, 55: 103– 119. Dingle, A. 2008. The effect of Nordmøre grid spacings on the reduction of bycatch in a northern NSW commercial estuarine prawn trawl fishery. MSc thesis, University of New England. 74 pp. FAO. 2007. The State of World Fisheries and Aquaculture. FAO, Rome. 131 pp. Ferro, R. S. T., and Xu, L. 1996. An investigation of three methods of mesh size measurement. Fisheries Research, 25: 171– 190. Halliday, R. G., and Cooper, C. G. 2000. Size selection of silver hake (Merluccius bilinearis) by otter trawls with square and diamond mesh codends of 55– 60 mm mesh size. Fisheries Research, 49: 77 – 84. Kelleher, K. 2005. Discards in the world’s marine fisheries. An update. FAO Fisheries Technical Paper, 470. 131 pp. 572 Kotz, S., Johnson, N. L., and Reid, C. B. 1982. Encyclopaedia of Statistical Sciences, 9. Wiley, New York. Kynoch, R. J., O’Dea, M. C., and O’Neill, F. G. 2004. The effect of strengthening bags on cod-end selectivity of a Scottish demersal trawl. Fisheries Research, 68: 249– 257. Lök, A., Tokaç, A., Tosunoğlu, Z., Metin, C., and Ferro, R. S. T. 1997. The effects of different cod-end design on bottom trawl selectivity in Turkish fisheries of the Aegean Sea. Fisheries Research, 32: 149– 156. Macbeth, W. G., Millar, R. B., Broadhurst, M. K., Hewitt, C. W., and Wooden, M. E. L. 2007. Intra-fleet variability in the size selectivity of a square-mesh trawl codend for school prawns (Metapenaeus macleayi). Fisheries Research, 86: 92 – 98. MacLennan, D. N. 1992. Fishing gear selectivity: an overview. Fisheries Research, 13: 201– 204. Millar, R. B., Broadhurst, M. K., and Macbeth, W. G. 2004. Modelling between-haul variability in the size selectivity of trawls. Fisheries Research, 67: 171– 181. Millar, R. B., and Fryer, R. J. 1999. Estimating the size-selection curves of towed gears, traps, nets and hooks. Reviews in Fish Biology and Fisheries, 9: 89– 116. Millar, R. B., and Walsh, S. J. 1992. Analysis of trawl selectivity studies with an application to trouser trawls. Fisheries Research, 13: 205–220. Ordines, F., Massutı́, E., Guijarro, B., and Mas, R. 2006. Diamond vs. square mesh codend in a multi-species trawl fishery of the western Mediterranean: effects on catch composition, yield, size selectivity and discards. Aquatic Living Resources, 19: 329– 338. Petrakis, G., and Stergiou, K. I. 1997. Size selectivity of diamond and square mesh codends for four commercial Mediterranean fish species. ICES Journal of Marine Science, 54: 13– 23. M. K. Broadhurst and R. B. Millar Reeves, S. A., Armstrong, D. W., Fryer, R. J., and Coull, K. A. 1992. The effects of mesh size, cod-end extension length and cod-end diameter on the selectivity of Scottish trawls and seines. ICES Journal of Marine Science, 49: 279 – 288. Robertson, J. H. B. 1986. Design and construction of square mesh cod-ends. Scottish Fisheries Information Pamphlet No. 12. Department of Agriculture and Fisheries for Scotland, Marine Laboratory, Aberdeen. 10 pp. Robertson, J. H. B., and Stewart, P. A. M. 1988. A comparison of size selection of haddock and whiting by square and diamond mesh codends. Journal du Conseil International pour l’Exploration de la Mer, 44: 148 –161. Sala, A., Lucchetti, A., and Buglioni, G. 2007. The influence of twine thickness on the size selectivity of polyamide codends in a Mediterranean bottom trawl. Fisheries Research, 83: 192– 203. Tokaç, A., Özbilgin, H., and Tosunoğlu, Z. 2004. Effect of PA and PE material on codend selectivity in Turkish bottom trawl. Fisheries Research, 67: 317– 327. Watson, J. W. 1989. Fish behaviour and trawl design: potential for selective trawl development. In Proceedings of the World Symposium on Fishing Gear and Fishing Vessels, pp. 25 – 29. Ed. by C. M. Campbell. Marine Institute, St Johns, Newfoundland, Canada. Wileman, D. A., Ferro, R. S. T., Fonteyne, R., and Millar, R. B. 1996. Manual of methods of measuring the selectivity of towed fishing gears. ICES Cooperative Research Report, 215. 126 pp. doi:10.1093/icesjms/fsp001
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