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Presentation - Gulf of Maine Research Institute

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Session 3: Broad Scale Stock Structure<br />

A summary and synthesis <strong>of</strong> Atlantic cod tagging<br />

studies, including movements<br />

Workshop on stock structure <strong>of</strong> Atlantic cod in the<br />

<strong>Gulf</strong> <strong>of</strong> <strong>Maine</strong> Region<br />

Portsmouth NH, June 12-14 2012<br />

Shelly Tallack<br />

<strong>Research</strong> Scientist - Applied Fisheries Ecologist<br />

350 Commercial Street, Portland, ME 04101 ・ tel: 207-772-2321 ・ fax: 207-772-6855 ・ www.gmri.org


Overview <strong>of</strong> cod tagging studies in the region, and available data


Tagging studies and data available for Atlantic cod since 2000<br />

Primary Organization<br />

/Contact<br />

Focus Tag type No. releases No. recaptures Dates<br />

GMRI and partners,<br />

Shelly Tallack<br />

Northeast Regional Cod<br />

Tagging Program: Movement<br />

patterns <strong>of</strong> cod throughout the<br />

<strong>Gulf</strong> <strong>of</strong> <strong>Maine</strong>, Canadian<br />

Maritimes and Southern New<br />

England waters<br />

T-bar tag (yellow, orange and<br />

blue)<br />

114,467 >6,700<br />

January 2003 – July 2005<br />

(tagging trips); program<br />

overall completed in 2011<br />

SMAST,<br />

David Martins/Steve<br />

Cadrin<br />

Movement <strong>of</strong> cod tagged in:<br />

Stellwagen Bank, Western<br />

Mass. Bay, Great South<br />

Channel, Georges Bank, Cape<br />

Ann.<br />

T-bar tags (yellow); DSTs in later<br />

years (2005 onwards) to<br />

address spawning fish<br />

movements<br />

>25,000* >1,160* August 2000 to present<br />

UNH,<br />

Hunt Howell<br />

Movement <strong>of</strong> cod tagged in<br />

Inshore GOM<br />

T-bar tag (yellow and orange) 24,466* 1,835* 2001-2004<br />

UNH,<br />

Hunt Howell<br />

Vertical activity and fine-scale<br />

distribution <strong>of</strong> cod in Ipswich<br />

Bay spawning ground<br />

DSTs & acoustic tags<br />

200 DSTs and 25<br />

acoustic<br />

26 DSTs (13%),<br />

plus live tracking<br />

<strong>of</strong> acoustic tags<br />

2006/2007<br />

DFO (St. Andrews),<br />

Don Clark<br />

Movement <strong>of</strong> cod tagged in the<br />

Bay <strong>of</strong> Fundy and on the Scotia<br />

Shelf<br />

T-bar tags (orange) 16,922* 715* 2000 – 2003<br />

Stellwagen Bank<br />

Nat. Mar. Sanct.,<br />

James Lindholm<br />

Site fidelity at deep boulder<br />

reefs & Site utilization in<br />

<strong>of</strong>fshore gravel habitat<br />

Acoustic tags 65 56 2003-2005<br />

SMAST,<br />

Doug Zemeckis<br />

Movements <strong>of</strong> spawning cod in<br />

WGOM<br />

Acoustic tags 63 22 2009-2011<br />

* Tag numbers reflect those data quality controlled and standardized into the same format as the larger Northeast Regional Cod Tagging Program (additional data may<br />

be available).


Data synopsis by region


Analyses undertaken to interpret movement & migration patterns<br />

• Fish size effects (sources for recaptures, by fish size)<br />

• Circular statistics on displacement (distance/direction)<br />

• Investigation into homing patterns<br />

• Seasonal effects (animations <strong>of</strong> seasonal recaptures)<br />

Mean distance moved (km)<br />

250<br />

200<br />

150<br />

100<br />

50<br />

0<br />

73-92cm<br />

Fall Fall Fall<br />

Recapture season


New analysis - Bivariate boxplot (bagplot) analysis<br />

• Acknowledgement: David Martins<br />

(formerly SMAST, now MA DMF).<br />

• A statistical approach to interpreting<br />

the dispersal <strong>of</strong> raw release and<br />

recapture data.<br />

• A bagplot = a convex polygon plotted<br />

around a bivariate median <strong>of</strong> a<br />

distribution (Rousseeuw et al., 1999).<br />

• Identifies areas <strong>of</strong> recapture density,<br />

but also outlier recaptures.<br />

Interquartile<br />

range<br />

Median dist.<br />

‘Fence’<br />

Outliers<br />

‘Inliers’ (~1.5 times<br />

interquartile range)


Western GOM / Inshore GOM<br />

• Few recaptures came from outside <strong>of</strong> the I GOM area; <strong>of</strong>fshore movements are<br />

outliers;<br />

• North-south ‘shuffle’ along the coast is evident;<br />

• Defined as ‘sedentary and resident’ by Howell et al. (2008);<br />

• Reiterated by analysis <strong>of</strong> combined NRCTP, UNH and SMAST data sets.


Western GOM / Inshore GOM


Western GOM / Inshore GOM – Recruitment from Cape Cod


Western GOM / Inshore GOM: Fine-scale studies<br />

• Fine-scale study in Ipswich Bay (Sicel<strong>of</strong>f<br />

& Howell, 2012):<br />

UNH acoustic tracking<br />

(Courtesy Hunt Howell & Laughlin Sicel<strong>of</strong>f)<br />

– Live tracking <strong>of</strong> acoustic tags (n=26)<br />

– DSTs (n=200 releases, 26 recaptures);<br />

• Verified that the spring spawning group:<br />

– Utilizes a limited area (


Scotian Shelf / Bay <strong>of</strong> Fundy / Browns Bank


Scotian Shelf / Bay <strong>of</strong> Fundy / Browns Bank<br />

• NRCTP releases in the B <strong>of</strong> F:<br />

– Most movements confined to the bay during spring/summer;<br />

– Southward movements to Georges Bank / Georges Basin in fall.<br />

– Little exchange with GOM; contrasts with mixing estimates <strong>of</strong> 15-20% by Hunt<br />

et al. (1999).<br />

• Historic studies: report a connection between Browns Bank and<br />

the ‘north’ (Scotian Shelf) and ‘north east’ (Bay <strong>of</strong> Fundy) (Higgins,<br />

1931).


Scotian Shelf / Bay <strong>of</strong> Fundy / Browns Bank<br />

• Releases in the B <strong>of</strong> F: move within the bay, and southwards towards deeper<br />

waters <strong>of</strong> Georges Basin; movements to GB are categorized as ‘outliers’.<br />

• Releases on Browns Bank: dispersed to Bay <strong>of</strong> Fundy, Georges Bank and<br />

central GOM.


Georges Bank


Georges Bank<br />

• Based on 1,086 recaptures:<br />

– Considerable cross-bank movement;<br />

– Some dispersal evident:<br />

• North to Bay <strong>of</strong> Fundy and CA waters<br />

• West to inshore waters.<br />

– But, <strong>of</strong>f-bank movements were found to be<br />

‘outliers’;


Cape Cod, Great South Channel, Nantucket Shoals, Block Island


Cape Cod, Great South Channel, Nantucket Shoals<br />

• High tagging effort by the NRCTP<br />

(>50,000 releases); these cod<br />

tended to be smaller (


Block Island<br />

• Relatively few cod found/tagged<br />

in this area until 2005 onwards;<br />

• Movements were mostly limited;<br />

those further afield were ‘outliers’.<br />

• In contrast to historic studies:<br />

little connection with southern<br />

waters <strong>of</strong> RI and NC (Higgins,<br />

1929; Schroeder, 1930)


Mid-Atlantic Bight (recaptures only)<br />

• Very little information<br />

for this area from<br />

studies since 2000;<br />

• Historic studies:<br />

– Linkages between<br />

southern MA waters and<br />

NC (Higgins, 1929)<br />

– Fall migration from<br />

Nantucket Shoals to<br />

RI/NC region<br />

(Schroeder, 1930).


Proposed “passages” <strong>of</strong> cod travel (raw data)<br />

GOM (5Y)<br />

SS (4X)<br />

GB (5Z)<br />

Sub-legal cod:<br />

• Recruiting to 2 stocks<br />

• Currently “GB/5Z”


Revised ‘passages’ <strong>of</strong> cod travel (after bagplots)


Attempts to quantify cod movements for application to stock<br />

assessments


Quantification <strong>of</strong> exchange between areas – GARM focused<br />

GOM (5Y)<br />

? %<br />

? %<br />

SS (4X)<br />

GB (5Z)<br />

What % is<br />

significant?


Attempts to quantify movements/mixing estimates<br />

• Two attempts on NRCTP data presented at the pre-GARM<br />

workshops:<br />

1. Tallack (2007, 2012): Weighting model(s)<br />

2. Miller & Tallack (2007): Finite-state continuous-time approach (FSTA)<br />

• FSTA model shows most promise for linking with current stock<br />

assessments because it also estimates F and M;<br />

• Further refinement needed for both models before either is<br />

conclusive.<br />

Miller T. & Tallack S. (2007), Estimating instantaneous rates <strong>of</strong> regional migration and mortality from conventional tagging data. DRAFT REPORT:<br />

Submitted to National Marine Fisheries Service, Pre-GARM working group, WP3D, October 2007. Northeast Fisheries Science Center, Woods Hole, MA:<br />

10 pp.<br />

Tallack, S.M.L., (2007). A description <strong>of</strong> tagging data from the Northeast Regional Cod Tagging Program (WP3A) and preliminary applications <strong>of</strong> weighting<br />

and mixing analysis (WP3C). DRAFT REPORT: Submitted to National Marine Fisheries Service, Pre-GARM working group. Northeast Fisheries Science<br />

Center, Woods Hole, MA, Working Papers 3A & 3C, 60 pp.<br />

Tallack, S.M.L., (2012). Stock identification applications <strong>of</strong> conventional tagging data for Atlantic cod in the <strong>Gulf</strong> <strong>of</strong> <strong>Maine</strong>. Submitted to: Advances in Fish<br />

Tagging and Marking Techniques, AFS, Proceedings from the International Symposium on 'Advances in Fish Tagging and Marking Techniques', Auckland,<br />

NZ, February 24-28th, 2008.


Major conclusions from tagging data with regard stock structure


Key conclusions from tagging data<br />

1. The connection between Cape Cod fish (5Z) and the Inshore<br />

GOM stocks (5Y) appears to be unquestionable - Inshore GOM<br />

fish appear relatively resident to the area, with additional<br />

recruitment <strong>of</strong> younger fish from waters around Cape Cod.<br />

2. Georges Bank fish are a largely self-sustaining <strong>of</strong>fshore<br />

population that mixes with the Scotian Shelf and Bay <strong>of</strong> Fundy<br />

fish.<br />

3. The Bay <strong>of</strong> Fundy retains a good portion <strong>of</strong> its cod, but mixing<br />

with the <strong>of</strong>fshore banks (Georges Bank and Browns Bank) is<br />

also evident.<br />

4. From recent movement studies, little can be said about cod in<br />

the Mid-Atlantic Bight and more southern waters.


Current and alternative stock management boundaries<br />

Alternative 1<br />

Current<br />

Alternative 2


Additional research required for stock structure determination


• Many gaps remain in our understanding <strong>of</strong> GOM cod population structure:<br />

– Some answers may come from additional analyses on current tagging data.<br />

– Additional integrated spatial studies are also needed (tagging, movement, genetic,<br />

habitat, environmental…).<br />

• Top research priority:<br />

“Recent and historical cod tagging data (and genetic data) suggest<br />

substantial movements across current stock boundaries and considerable<br />

heterogeneity within current management units. Best available science<br />

indicates the need to re-visit, re-analyze and re-assess the stock<br />

management boundaries.”<br />

Tallack, S.M.L., 2009. Proceedings from a workshop to identify future research priorities for cod tagging in the <strong>Gulf</strong> <strong>of</strong> <strong>Maine</strong>. Northeast Fisheries Science<br />

Center Reference Document. US Department <strong>of</strong> Commerce, 09-09, 76 pp.


Key research needs outlined<br />

• Theme 1 – Cod Management:<br />

– Interdisciplinary assessment <strong>of</strong> cod management boundaries;<br />

– Investigate options for alternative management scales;<br />

– Expand research to earlier life-stages.<br />

• Theme 2 – Data mining, re-analysis, modeling:<br />

– Meta-analysis <strong>of</strong> historical mark-recapture datasets (particularly for the period<br />

since 2000);<br />

– Stock assessment applications <strong>of</strong> tagging data and parameters we can derive<br />

from these data, e.g. natural mortality, fishing mortality, growth, selectivity.<br />

• Theme 4 – Reporting rates/outreach efficacy – to improve our<br />

interpretation <strong>of</strong> tagging data.


Key research needs outlined (cont.)<br />

• Theme 5 – Additional deployment <strong>of</strong> tags on cod:<br />

– Juvenile cod: habitat usage, movements, dispersal from nursery grounds to<br />

adult stocks;<br />

– Spawning cod: address all major spawning grounds to investigate, natal<br />

homing, long-term spawning movements, timing <strong>of</strong> spawning, critical habitats,<br />

etc.;<br />

– Fine-scale investigations to improve our understanding <strong>of</strong> critical habitats;<br />

– Multi-year, long-term tagging with consistent tag releases over time and by<br />

area;<br />

– Advanced tagging technologies, e.g. acoustic arrays in strategic areas;<br />

– Closed-area investigations: critical habitat, size, timing, etc;<br />

– Incorporate additional ecology & biology within future tagging studies.


Acknowledgements<br />

• Analytical contributions by: Steve Cadrin (SMAST), Mark Terceiro<br />

(NEFSC), Loretta O’Brien (NEFSC), Ralph Mayo (NEFSC), Tim Miller<br />

(NEFSC), David Martins (MA DMF), and Don Clark (DFO).<br />

• Data contributions by: Northeast Regional Cod Tagging Program; Hunt<br />

Howell (UNH); Don Clark (DFO); David Martins (SMAST).<br />

• These studies would not be possible without the effort invested by various<br />

funding bodies, including NOAA’s Cooperative <strong>Research</strong> Program, and<br />

numerous scientists and members <strong>of</strong> the commercial and recreational<br />

fishing industry. See www.codresearch.org for full list.<br />

~50 scientists >106<br />

vessels

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