A One Blue Cod Characterisation - Nz Sport Fishing
June 2015 APPENDIX ONE: BLUE COD FISHERY CHARACTERISATION In support of the Marlborough Sounds blue cod regulatory review DRAFT – FOR THE BLUE COD MANAGEMENT GROUP ONLY 1
CONTENTS Introduction . 4 Biology of Blue Cod . 5 Overview of Recent Research and Management . 7 Fishery Research . 8 Surveys. 9 Catch Rates . 10 Ageing . 14 Sex Ratio . 14 Fish Under 30 cm . 15 Catch Limits and Allowances . 17 Sector Profiles . 18 Commercial Profile . 19 Overview . 19 Estimated Catches by Statistical Area . 20 Commercial Use . 23 Commercial Regulations. 26 Recreational Profile . 28 Overview . 28 Summary of Recreational Regulations . 28 Recreational Harvest Estimates . 31 Location of Recreational Fishing in Marlborough Sounds . 33 Recreational Fisher Representation . 34 Amateur‐Fishing Charter Vessel Reporting Information. 34 Recreational Motivations and Perception . 36 Recreational Value . 37 Blue Cod Incidental Mortality from Recreational Fishing . 38 Customary Profile. 39 Overview . 39 Customary Fishing . 40 Customary Fishing Regulations . 40 Customary Harvest . 40 Mātaitai Reserves and Taiāpure . 41 Fishery Compliance . 42 Overview . 42 Offences . 42 Effective Deterrent. 45 Information and Education . 46 Appendix One: Blue Cod Fishery Characterisation, June 2015 · 2
Monitoring and Surveillance. 46 Deterrence . 48 Spatial Management. 49 Marine Reserves. 49 Other Impacts . 52 Sedimentation and Pollution . 52 Invasive Species . 53 Marine Farms . 53 Other Fishing Impacts . 54 Intrinsic Value . 56 Annex One . 58 References . 59 Appendix One: Blue Cod Fishery Characterisation, June 2015 · 3
INTRODUCTION Blue cod are often considered to be the most important recreational finfish species in the South Island. They are an iconic species in the Marlborough Sounds Area and Challenger (East) area, where they have become a topic of much concern over the years given the strong recreational fishing pressure in this area and their vulnerability to localised depletion. The Blue Cod Management Group was formed late in 2008 by the then Minister of Fisheries. They were tasked with developing a management plan for the recreational blue cod fishery in the Marlborough Sounds Area to support its reopening after it was closed in 2008. The Group finished their plan in 2010, and the fishery was reopened with a suite of management measures in 2011 following consultation. The Group is now tasked with undertaking a review of rules that have been in place since 2011. This document characterises the blue cod fishery in the Marlborough Sounds Area and Challenger (East) area with the best information available at the time of writing. It is intended to support the 2015 review of the blue cod fishing rules by providing a foundation of information while considering potential options for the future management of the fishery. Appendix One: Blue Cod Fishery Characterisation, June 2015 · 4
BIOLOGY OF BLUE COD Blue cod (Parapercis colias) is a bottom‐dwelling species endemic to New Zealand. It is not a true cod, but a member of the weaver family (also known as a sandperch). This species is distributed throughout New Zealand near foul ground to a depth of 150 m, and is most abundant south of Cook Strait and around the Chatham Islands. In the Marlborough Sounds Area, blue cod are associated with habitat comprised of jagged bedrock, sand, shell hash, and also tube worms. These types of habitats are considered to be complex and heterogeneous (made up of multiple different components), and are particularly important for blue cod. Blue cod are typically absent from ‘homogeneous’ (similar or few components) sand habitats. Blue cod are relatively slow growing and long lived. The growth rate of blue cod differs across locations1 and between sexes (with males typically growing faster and to a larger size than females2). The maximum recorded age for this species is 32 years. Size‐at‐sexual maturity also varies according to location. In the Marlborough Sounds Area it is estimated to be reached at 21 ‐ 26 cm total length (TL) at 3‐6 years3. Hermaphrodites have both functional male and female reproductive organs at some point in their life. Blue cod are protogynous hermaphrodites4. This means that females are capable of changing sex from female to male, and then reproduce as males (though not all females change sex). Size‐at‐sex change is also variable, and is likely to be influenced by social and behavioural cues. Males that are derived from sex changed females are known as secondary males. However, not all male blue cod are derived from sex change. A proportion of the population is comprised of primary males, which sexually differentiate as males from larvae, and never go Appendix One: Blue Cod Fishery Characterisation, June 2015 · 5
through a female stage. This is called diandry (when individuals may start life as either sex, as opposed to monandry, where all individuals start life as the same sex). The rate of recruitment of primary males and secondary males into a population determines the overall sex ratio of a population. What determines how many fish will become primary males or change sex into secondary males is an important but complicated question. There is evidence to suggest that the sexual differentiation of larvae of protogynous hermaphrodites into male or female is influenced by external social cues, such as the population size present on the reef when larvae settle (and is not genetically predetermined)5, 6. Given that the rate of recruitment of primary males appears to fluctuate in the Marlborough Sounds Area, it is possible that sexual differentiation of larvae into males or females is influenced by external cues in these populations. The rate of sex change (recruitment of secondary males) is also variable. Sex change is thought to be most strongly influenced by the presence of socially dominant males7, as they prevent females from changing sex. As a result, removing large blue cod from the population may remove dominant males and lead to more females changing sex at smaller sizes6. This can have knock‐on effects on the overall reproductive output of a population; less females means there will be less eggs overall to be fertilized and contribute to the next generation. Blue cod have an annual reproductive cycle with an extended spawning season during late winter and spring. Spawning aggregations have been reported within inshore and mid shelf waters, but likely occurs in outer shelf waters. Ripe blue cod are found in all areas fished commercially by blue cod fishers during the spawning season. Eggs are pelagic (in the water column) for about five days after spawning, and the larvae are pelagic for about five more days before settling onto the seabed. Distribution of blue cod populations is localised. Tagging experiments carried out in the Marlborough Sounds Area in the 1940s and 1970s found that most blue cod remained in the same area for extended periods, though some individuals moved away from the reef or headland where they were tagged (mean distance of 7.6 km)8. A more recent tagging experiment carried out in Foveaux Strait showed that although some blue cod moved as far as 156 km, 60% travelled less than 1 km9. A similar pattern was found in Dusky Sound where four fish moved over 20 km, but 65% had moved less than 1 km10. Larger movements observed during this study were generally eastwards into the fiord. The inner half of the fiord was found to drain the outer fiord, and had 100% residency. Anecdotal evidence suggests that blue cod will form mass migrations from time to time, but evidence of this is rare relative to studies suggesting high localised residency for the majority of blue cod in a population. Blue cod are fairly generalist predators, eating a variety of prey including small crustaceans, molluscs (including octopus), fish, polychaetes, and echinoderms11, 12, 13. Diet tends to differ across environmental gradients and between separate locations subject to prey availability. They are known by fishers to be voracious and non‐selective feeders that easily take bait. Overall, the biological characteristics of blue cod, including hermaphroditism, localised populations, and generalist feeding habits, make them susceptible to the effects of fishing and to localised depletion. Appendix One: Blue Cod Fishery Characterisation, June 2015 · 6
OVERVIEW OF RECENT RESEARCH AND MANAGEMENT 2004 – Fixed‐site abundance survey repeated (Separation Pt included). Substantial drops in catch rates in Queen Charlotte & Pelorus from previous survey. 1996 – Fixed‐site abundance survey repeated including all of Pelorus and east D’Urville. 1995 – Fixed‐ site abundance survey in Queen Charlotte and outer Pelorus Early 1990s – Sustainability concerns present for the MS recreational blue cod fishery. 2001 – Fixed‐site abundance survey repeated for Queen Charlotte, Pelorus, and east D’Urville. 1995 – TACC reduced to 70t 1993 – Bag limit reduced from 12 to 10; TACC set at 95 t. 1 October 2008 – Recreational fishery closed in the inner MS to protect the future of the fishery. 2010 – Fixed‐site survey repeated. Catch rates increased markedly Queen Charlotte and Pelorus Sounds, remained constant in D’Urville 2012 – Recreational fishers express concerns about effectiveness of the 2011 rules 2014 – BCMG tasked with reviewing management plan for the fishery & reinvigorated with new representation and expanded scope 2008 – Cook Strait fixed site abundance survey 2007 – Fixed site abundance survey repeated (Separation Pt excluded) 2003 – Bag limit reduced from 6 to 3 in the MS and 10 to 3 in Challenger East. MLS increased from 27 to 30 cm in MS & reduced from 33 to 30 cm for rest of Challenger East. 1996 – bag limit reduced from 10 to 6 Present 2010 – BCMG Management Plan finalised & review of recreational regulatory measures completed March 2009 – Marlborough Sounds Blue Cod Management Group established and tasked with developing a management plan to support a lifting of the closure earlier than the scheduled date of 1 October 2012 2013 – Abundance survey brought forward 1 year. Catch rates declined in Queen Charlotte and Pelorus relative to 2010, but were higher than in 2001 – 2007. Catch rates constant in D’Urville, and declined in Cook Strait between 2010 and 2013 (only 2 comparable years) 1 April 2011 – Fishery reopened with a package of management measures in place for the MSA (including bag limit 2, slot limit, transit rule, seasonal closure, hook limit, no accumulation, and requirement to land in whole or gutted state):
FISHERY RESEARCH The Marlborough Sounds Area and Challenger (East) area is part of the wider ‘BCO 7’ fishstock (see Figure 6 for a map of the area). The status of blue cod in the wider BCO 7 management area is currently unknown. No BMSY proxy target reference level has been set for BCO 7, and it is unknown where the current stock size is in relation to a target or other limits. However, there is currently no information to suggest a stock‐wide sustainability issue. There are concerns about the health of the blue cod fishery in the Marlborough Sounds Area. Periodic relative abundance potting surveys are used to provide information on the abundance, sex ratio, size frequency, and age frequency of blue cod populations in this area over time. This enables the Ministry for Primary Industries (MPI) to monitor changes in relative abundance and the other parameters outlined above over time, to understand how the fishery is responding to fishing pressure. These potting surveys are currently considered to be the most effective way of collecting this information. The surveys have been conducted for a number years in a row and therefore provide an important time series for relative abundance. Appendix One: Blue Cod Fishery Characterisation, June 2015 · 8
SURVEYS Eight surveys have been conducted for blue cod in and around the Marlborough Sounds Area and west D’Urville Island, with some differences over the years (Table 1)14, 15, 16, 17, 18, 19. Table 1: Surveys conducted in the Marlborough Sounds Area and Challenger (East) area by year, and regions sampled. Year 1995 1996 2001 2004 2007 2008 Area Surveyed Queen Charlotte Sound Pelorus Sound Outer only Comments D’Urville Island East only East only Cook Strait 2010 2013 Included Separation Point Separation Point dropped 2001 and 2008 surveys reanalysed so that they were consistent with methods used for recent surveys 1995 and 1996 surveys reanalysed For the purpose of these surveys, the whole area is split into smaller survey areas, called strata (Figure 1), within which a number of sites are used for sampling. All surveys before 2010 used fixed sites that were selected randomly from a wider list of fixed sites within a given stratum (Figure 1). These fixed locations are available to be used repeatedly on subsequent surveys in that area.20 In 2010, a suite of random locations were added to the fixed sites in selected strata. Random sites may have any location and are generated randomly within each stratum. In 2013, full random and full fixed site surveys were conducted. However, only the fixed site components of the 2010 and 2013 surveys are considered comparable to the earlier surveys. The gradual shift to a random site survey has come about as a result of an international review and recommendations for methodology. The use of the random site methodology is experimental, and the MPI Science Working Group is yet to determine if the random methodology will be a useful way to survey the fishery in the future. MPI is proposing to carry out three separate surveys before considering a move to a random survey design. The use of a multibeam sonar system to identify suitable blue cod habitat in the 2013 survey means that the results from this survey were comparable to results from previous surveys, despite involving a new skipper. Blue cod pots can draw fish in from some distance away, and the same pot design has been used for each fixed site survey. Appendix One: Blue Cod Fishery Characterisation, June 2015 · 9
Figure 1: All possible fixed sites (left) and research strata (right) available for the blue cod relative abundance potting surveys in the Marlborough Sounds. CATCH RATES Throughout the potting surveys, catch rates of total and “recruited” blue cod (30 cm and over in length) have been similar between Queen Charlotte Sound and Pelorus Sound, highest around D’Urville Island, and lowest in Cook Strait (Figures 2 to 5; Table 4). Queen Charlotte Sound and Pelorus Sound In April 2011, a suite of management measures was introduced for recreational fishers for the Marlborough Sounds Area (Figure 6). The 2013 potting survey was carried out two years after the management regime had been in place, with recruited blue cod catch rates for both Queen Charlotte and Pelorus Sounds declining compared to 2010, but remaining higher than 2001 to 2007, when the fishery was open (Figures 2 and 3). Catch rates by stratum and size class indicate that catches tended to be higher in the outer strata for all size classes in the 2013 survey (Table 2). Table 2 also shows how catch rates have changed amongst strata and between years (2007, 2010, and 2013 surveys). Appendix One: Blue Cod Fishery Characterisation, June 2015 · 10
Figure 2: Scaled catch rates of blue cod from Queen Charlotte Sound fixed sites from 1995 to 2013. Catch rates are shown for all blue cod, blue cod within the slot limit (30-35 cm), recruited blue cod (35 cm over), and for pre-recruited blue cod (under 30 cm). Error bars are 95% confidence intervals. NOTE: the catch rate scale differs from other figures and goes from 0 – 3.0. Figure 3: Scaled catch rates of blue cod from Pelorus Sound fixed sites from 1996 to 2013. Catch rates are shown for all blue cod, blue cod within the slot limit (30-35 cm), recruited blue cod (35 cm over), and for pre-recruited blue cod (under 30 cm). Error bars are 95% confidence intervals. NOTE: the catch rate scale differs from other figures and goes from 0 to 4.0 Appendix One: Blue Cod Fishery Characterisation, June 2015 · 11
D’Urville Island In the D’Urville Island strata, catch rates for recruited blue cod between 2004 to 2013 have been stable (Figure 4). D’Urville was not closed to fishing in October 2008, but D’Urville East was included in the management area where specific measures have been applicable since April 2011. Catch rates tended to be higher in D’Urville alongside the other outer strata than in the inner sounds for all size classes in 2013 (Table 2). Figure 4: Scaled catch rates of blue cod from D’Urville region fixed sites from 2004 to 2013. Catch rates are shown for all blue cod, blue cod within the slot limit (30-35 cm), recruited blue cod (35 cm over), and for pre-recruited blue cod (under 30 cm). Error bars are 95% confidence intervals. NOTE: the catch rate scale differs from other figures and goes from 0 to 6.0 Appendix One: Blue Cod Fishery Characterisation, June 2015 · 12
Cook Strait Cook Strait has had only two comparable surveys using a random design (2010 and 2013). The first survey in 2008 was a fixed site survey. Recruited blue cod catch rates from the random survey years were higher in 2010 in comparison to 2013 (Figure 5). The Cook Strait region has not been subject to the same rules that have applied to the Marlborough Sounds Area. Cook Strait (random sites) 1.6 All blue cod Catch rate (kg.pot ‐1) 1.4 30–35 cm (slot) 1.2 over 35 cm 1.0 under 30 cm 0.8 0.6 0.4 0.2 0.0 1995 1996 2001 2004 2007 2008 2010 2013 Year of survey Figure 5: Scaled catch rates of blue cod from Cook Strait region random sites in 2010 and 2013. Catch rates are shown for all blue cod, blue cod within the slot limit (30-35 cm), recruited blue cod (35 cm over), and for pre-recruited blue cod (under 30 cm). Error bars are 95% confidence intervals. NOTE: the catch rate scale differs from other figures and goes from 0 to 1.6 Appendix One: Blue Cod Fishery Characterisation, June 2015 · 13
Table 2: Mean catch rates (kg.pot-1) for blue cod by size category and for individual strata from the 2013 Marlborough Sounds fixed-site potting survey. Catch rates are pot-based. (Note: 2013 CVs are set-based and range from 12.6 - 58.6% for fish under 30 cm, 14.8 - 74.8% for 30-35 cm, and 29.1 - 100.0% for fish over 35cm.) Strata considered to be in the ‘outer Sounds” are shaded dark blue, and ‘inner Sounds’ strata are shaded light blue (see Figure 1). 30 cm 30 – 35 cm 35 cm 2007 2010 2013 2007 2010 2013 2007 2010 2013 Inner Queen Charlotte Outer Extreme Sound Outer Inner Pelorus Sound D’Urville 0 0.12 0.19 0 0.28 0.08 0 0.2 0.06 0.43 0.37 0.33 0 1.02 0.46 0.19 1.16 0.32 0.67 0.38 0.21 0.34 0.43 0.62 1.57 1.06 0.26 0.17 0.25 0.20 0.00 1.09 0.11 0.11 1.14 0.03 Middle 0.18 0.22 0.17 0.00 0.53 0.34 0.21 0.85 0.12 Outer Extreme Outer East 0.34 0.31 0.52 0.03 1.13 1.35 0.43 2.42 0.63 0.77 0.72 1.31 0.16 0.29 2.32 2.26 2.52 1.32 0.60 0.79 1.10 0.50 0.27 1.54 1.87 1.08 0.75 West 0.89 1.37 1.26 1.38 1.18 2.28 3.19 3.09 1.01 AGEING No ageing results, including estimates of total mortality (Z) and spawner biomass per recruit, are presented here from the 2013 survey because they are under consideration by the MPI Science Working Group. The age distributions derived from the 2013 survey differed substantially from those obtained in previous surveys. Therefore, an ageing protocol for blue cod is under development, and this will ensure ageing methodology is applied consistently across all future blue cod studies. Ageing results for the 2013 survey will be reassessed against this protocol once it is complete. SEX RATIO Regional sex ratios have been dominated by males over all surveys, apart from D’Urville Island in 2004 when it was 50% male (Table 4). Analysis at the strata level shows that sex ratios are also dominated by males apart from a handful of examples (Table 3). This is unusual, and a higher proportion of females to males would typically be expected in a natural population. The reasons for these sex ratios are not clear, as there are other impacts that may affect the blue cod populations in area other than fishing pressure (see Other Impacts). A high ratio of males to females is considered indicative of a heavily fished population18. Appendix One: Blue Cod Fishery Characterisation, June 2015 · 14
The 2013 fixed‐site survey indicates that sex ratio varies depending on location, with males dominating the sex ratio in most strata (Table 3). Sex ratio also varies depending on size class (Table 3). Table 3: Sex ratios (percent male) for blue cod by size category for individual strata, for the fixedsite 2013 Marlborough Sounds potting survey. Sex ratios are shown in bold and the sample size is shown in brackets (the number of fish the sex ratio was able to be derived from). 30 cm Inner 35 cm 2007 2010 2013 2007 2010 2013 2007 2010 2013 n/a (0) 46.8 (19) 46.2 (15) n/a (0) 68.9 (16) 100 (6) n/a (0) 100 (15) 100 (2) 35.2 (57) 45.2 (59) 81.1 (15) 75.1 (99) 41.3 (83) n/a (0) 88.1 (58) 82.4 (25) 53.5 (58) 94 (13) 90.7 (143) 90.3 (105) 86.5 (39) 100 (18) 96.9 (32) 100 (9) Queen 48.8 Charlotte Outer (60) Sound Extreme 61.4 Outer (103) Pelorus Sound 30 – 35 cm Inner 53.3 (22) 50.2 (16) 89.4 (19) 70.9 (7) 94.7 (54) 84.1 (6) n/a (0) 100 (37) 100 (1) Middle 50.1 (51) 45.9 (37) 70.9 (15) 80.2 (21) 87.2 (70) 94.7 (20) n/a (0) 100 (29) 51.1 (3) Outer 57.0 (122) 69.7 (39) 80.8 (38) 93.9 (70) 90.4 (165) 97.4 (79) 100 (3) 100 (51) 100 (19) Extreme 73.9 Outer (192) 71.2 (69) 72.6 (87) 96.1 (334) 90.4 (168) 93.7 (146) 100 (17) 100 (14) 100 (42) East 58.4 (220) 43.2 (154) 66.7 (74) 77.9 (418) 68.8 (122) 76.7 (102) 95.1 (74) 93.9 (17) 100 (24) West 52.2 (233) 56.0 (384) 50.4 (74) 70.1 (589) 70.3 (541) 68.2 98.0 94.9 (151) (150) (119) 93.3 (31) D’Urville FISH UNDER 30 CM The type of pots used to survey blue cod in the Marlborough Sounds has been consistent across all the surveys so as to make results comparable within the time series. However, these pots do not retain many fish under 30 cm because of escape gaps. There are two methods available to MPI for investigating this information. The available information on fish under 30 cm caught in pots may underestimate the overall abundance, but it still provides some indication of relative abundance when viewed across a time series, as the methodology is consistent across this time (Figures 2 – 5). However, it is not clear if there is any inherent bias in sampling sex ratio of these smaller siz
DRAFT - FOR THE BLUE COD MANAGEMENT GROUP ONLY 1 In support of the Marlborough Sounds blue cod regulatory review APPENDIX ONE: BLUE COD FISHERY CHARACTERISATION June 2015. Appendix One: Blue Cod Fishery Characterisation, June 2015 · 2 CONTENTS
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