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An Overview of Methods for Estimating Absolute Abundance of Red Snapper in the Gulf of Mexico JM Drymon 1 , Greg Stunz 2 1. Mississippi State University, Coastal Research and Extension Center 2. Harte Research Institute, Texas A&M University-Corpus Christi Photo by Mike Kittrell

An Overview of Methods for Estimating Absolute …. Drymon for...An Overview of Methods for Estimating Absolute Abundance of Red Snapper in the Gulf of Mexico JM Drymon 1, Greg Stunz

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Page 1: An Overview of Methods for Estimating Absolute …. Drymon for...An Overview of Methods for Estimating Absolute Abundance of Red Snapper in the Gulf of Mexico JM Drymon 1, Greg Stunz

An Overview of Methods for Estimating Absolute

Abundance of Red Snapper in the Gulf of

Mexico JM Drymon1, Greg Stunz2

1. Mississippi State University, Coastal Research and Extension Center

2. Harte Research Institute, Texas A&M University-Corpus Christi

Photo by Mike Kittrell

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The Issue

The Project

The Methods

Photo by Brian Jones

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The Issue• Historical overfishing

led to depletion of the Gulf of Mexico red snapper stock

• Despite decreased season lengths, the stock remains overfished

• Recreational anglers perceive a healthy stock

• This has lead to mistrust between recreational anglers and federal managersPhoto by David Hay Jones

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The Project

• Congress made available funding to independently estimate red snapper abundance

• Two year project: starts in 2017, to be completed by 2019

• Well-integrated, multi-disciplinary team of investigators

Photo by David Hay Jones

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The Methods

1. Habitat mapping

2. Tagging

3. Direct counts

4. Depletion methods

Photo by David Hay Jones

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1 23

4

Habitat Mapping:Ecological Boundaries

Grouping variables• Sediment type (% cover of sand, mud, gravel, rock)• Artificial reefs + platforms (based on 0.2 degree cell grid of the shelf)• Turbidity• Dissolved Oxygen

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Habitat Mapping

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Habitat Mapping

• Sources: bathymetry data; multi-beam and side-scan sonar imagery

• Calculate the extent of natural hard bottom substrates and unknown/unconsolidated bottom habitats

• Quantify the number of existing artificial reef structures

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• Select random reef sites for tagging

• Tag no more than five red snapper per reef

• One-third of all fish get double tagged

750 fish tagged immediately prior to season opening

Tagging: Proof of Concept

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Tagging: Results

3 weeks - 724 fish tagged

Photo by David Hay Jones

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Photo by David Hay Jones

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How does the model work?

Alive

Dead

Caught

Not Caught

Caught

Not Caught

RetainTag

LostTag

Stay

Move

RELEASED

Not Reported

Not Reported

λ

REPORTED

REPORTED

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• We’ve demonstrated proof of concept for this method (2016, 2017)

• Estimated exploitation using a conceptually straight-forward approach that engaged the recreational angling community

Sackett DK, Catalano M. 2017. Spatial heterogeneity, variable rewards, tag loss, and tagging mortality affect the performance of mark–recapture designs to estimate exploitation: an example using red snapper in the northern Gulf of Mexico. North American Journal of Fisheries Management 37(3).

Sackett DK, Catalano MC, Drymon JM, Powers SP. In review. Estimating red snapper exploitation rates using a high-reward tag-recapture approach: insights into the Alabama red snapper fishery. Marine and Coastal Fisheries.

Photo by David Hay Jones

Tagging

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Estimating Population Size

• There are two general approaches to estimating population size:

1. Make a direct count of fish in a defined area (or make a count that needs to be adjusted to account for gear efficiency)

2. Note how removals (i.e. depletions) affect an index of relative abundance

2a. Change-in-ratio2b. Index Removal2c. Removal Estimators

Photo by Mike Kittrell

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• Remotely operated vehicles (ROVs) and towed camera arrays

• Testing to determine the area “sampled” and gear affects (attraction, avoidance)

Lembke C, Grasty S, Silverman A, Broadbent H, Butcher S, Murawski S. 2017. The camera-based towed assessment survey system (C-BASS): a towed camera platform for reef fish abundance surveys and benthic habitat characterization in the Gulf of Mexico. Continental Shelf Research 151: 62-71.

What about the fish you don’t see?

Direct Counts

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• Depletion methods use a known removal to adjust an index of relative abundance.

• Change-in-Ratio, Index-Removal, and Removal Estimators

• Change-in-Ratio: calculates how a known, selective removal (e.g. legal size fish) changes the ratio of the population in two classes (legal and sublegal).

• Index removal: survey-removal-survey

Depletion Methods

Photo by David Hay Jones

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Change in Ratio

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Change in Ratio

Carleton LM, Drymon JM, Powers SP, Mareska J, Walter M, Lauretta MV, Hoenig JM. 2015. Evaluating effects of recreational fishing at red snapper hot spots using change-in-ratio and Index-Removal methods. Annual Meeting of the American Fisheries Society, Portland, Oregon.

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Index-Removal

Carleton LM, Drymon JM, Powers SP, Mareska J, Walter M, Lauretta MV, Hoenig JM. 2015. Evaluating effects of recreational fishing at red snapper hot spots using change-in-ratio and Index-Removal methods. Annual Meeting of the American Fisheries Society, Portland, Oregon.

• Index-removal looks at how an index (of relative abundance) changes due to a known removal.

• Let’s assume catch is proportional to abundance.

• Then a (camera) survey indicates an index of relative abundance of 40 fish per unit effort.

• Subsequent (VL) harvest captures 100 fish

• The following (camera) survey indicates an index of relative abundance of 20 fish per unit effort: i.e. the relative abundance declined by half.

• We can then infer that 100 animals represents half of the initial population size, i.e. the initial population size was 100/0.5, or 200.

Photo by David Hay Jones

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Index-Removal

Hoenig JM, Pollock KH. 1998. Index-removal Methods. Invited article for the Encyclopedia of Statistical Sciences Update Volume 2 pp. 342-346 (S. Kotz, C.B. Read and D.L. Banks, editors). John Wiley and Sons, Inc., New York.

• Hoenig and Pollock (1998) provide assumptions for this method:

• 1. Closed population except for the removals

• 2. All animals have the same probability of capture, and this probability doesn’t vary between surveys

• 3. Sampling is with replacement, or the fraction of the population removed is negligible.

• When assumptions of CIR and IR are met, IR is more precise

Photo by David Hay Jones

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• Gulf of Mexico red snapper remains overfished, yet recreational anglers perceive a healthy stock; this has lead to mistrust between recreational anglers and federal managers

• Consequently, Congress funded a multi-disciplinary team of experts to independently estimate the abundance of the stock

• Habitat-specific methods will be tested and employed

• High-reward tagging, direct counts and depletion methods

In Summary

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Acknowledgements