Linear and non-linear responses of marine and coastal fish populations to physics and habitat: a view from the virtual world

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Linear and non-linear responses of marine and coastal fish populations to physics and habitat: a view from the virtual world Kenneth Rose Dept. of Oceanography & Coastal Sciences Louisiana State University

https://beya.io/2016/03/complicated-vs-complex-and-why-it-matters/

http://en.wikipedia.org/wiki/logistic_map 100 generations r 0 to 4

4

Example 1 - Shrimp Roth, B.M., K.A. Rose, L.S. Rozas, and T.J. Minello. 2008. Marine Ecology Progress Series 359: 185-202

Coastal Louisiana Trends: 1956-2050 Land Loss 1956-2000 Predicted Land Loss 2000-2050 Land Gain 1956-2000 Predicted Land Gain 2000-2050

Introduction Linkages between marsh habitat and nekton abundance brown shrimp blue crab Land Lost to Water 1950 2000 spotted seatrout Abundance (#/ha) Edge Habitat Percent marsh Percent marsh Sources: Minello and Webb 1997, Minello and Rozas 2002, Zimmerman and Minello 1984

Model description Study locations Galveston Bay, TX Caminada Bay, LA

Model description Creating 3D Marshscapes 500m Caminada Bay, LA 1 pixel = 1m

Model description Inundation Height (cm) relative to marsh edge 50.0 40.0 30.0 20.0 10.0 0.0-10.0-20.0-30.0-40.0 Cut bank Gradual 20m 10m 9m 8m 7m 6m 5m 4m 3m 2m 1m Edg 1m 2m 3m 4m 5m 6m 7m 8m 9m 10m Distance from marsh edge (m) Water depth (cm) 75 50 25 0-25 -50-75 0 20 40 60 80 100 Julian Day Louisiana Texas

Model description Model Weekly Cohort introduction Hourly Movement Mortality Growth rate Initial location Attraction Water levels Emergency Size, movement, habitat Size Attraction Random Depth 70mm? Growth Location, density, temperature Export Growth production Trophic transport

Corroboration: Density Patterns Rising High Low Falling

Landscape metrics Landscape influences shrimp export Number of sub-adult exports (thousands) 650 600 550 500 450 400 350 650 600 550 500 450 400 350 0 10 20 30 Edge distance (km) 2 4 6 8 10 12 14 16 18 Landscape Shape Index 0.86 20 40 60 80 Percent marsh 0.88 0.90 0.92 0.94 Clumpiness 0.96 0.98

Constructed marshes Do these marshes function similarly?? = Courtesy of Lawrence Rozas Terraced marsh in Galveston Island State Park

Example 2: Spiny Lobster Butler, M.J., J.H. Hunt, W.F. Herrnkind, K.A. Rose, and T. Dolan. 2005. Ecological Applications 15:902-918.

Spatial Structure of Individual-Based Spiny Lobster Recruitment Model

Individual-based Population Dynamics 28 Day Loop Day Loop Settlement Growth Emigration empirically-based probability functions daily time step for each individual in model for specified number of yrs (e.g. ~ 10 million individuals in a 10 year simulation) Mortality Shelter Selection PaV1 Disease

Shelter Selection Leave lobster in seagrass Have all lobsters been examined? Is lobster in Seagrass? Settlement Routine Mortality Routine Lobster s shelter is macroalgae Is lobster < 12mm CL? Move lobster to postalgal shelter? Determine postalgal shelter prob. Is lobster 12 25 mm CL? Put lobster in next preferred shelter Enough of next preferred shelter? Lobster remains n the open with little shelter Last shelter on preference list?

Massive Habitat Loss Blue-green algal blooms killed about 60% of all sponges in bloom-impacted areas 1991: November 15 through January 2 1992: October 1 through January 27

M ean Num ber of lobsters / cell Predicted Effect of Bloom on Lobster Shelter Use Perturbed Region 20 15 10 5 O pen Loggerhead Sponges O ther Sponges Solution Holes O ther Shelters 0 1988 1990 1992 1994 1996 1998 (Bloom periods are shaded red)

Predicted Effect of Habitat Change on Juvenile Lobster Abundance Mean No. Lobsters / Cell 20 18 16 14 12 10 8 6 4 No Bloom Bloom Entire M odel Region 2 0 1988 1990 1992 1994 1996 (Bloom periods are shaded red)

Example 3: Croaker Rose, K.A., S. Creekmore, D. Justic, P. Thomas, J.K. Craig, R. Miller Neilan, L. Wang, Md S. Rahman, and D. Kidwell. In review. Modeling the population effects of hypoxia on Atlantic croaker (Micropogonias undulatus) in the northwestern Gulf of Mexico: Part 2 Realistic hypoxia and eutrophication 25

Model Overview Spatially explicit, IBM Follows 7 stages to age 8 September 1 birthday Model year begins Sept. 1 Each year 365 days long Hourly processes Growth Mortality Reproduction Movement (routine & avoidance) Ocean Larva Yolk Sac Larva Estuary Larva Adult Environmental conditions simulated on a 2-D spatial grid Climatological temperature Climatological surface Chl-a Dissolved oxygen from 3-D hydrodynamics-wq model Egg Early (< 97mm) Juvenile Late Juvenile (< 180mm) 26

Model Grid Idealized 300 x 800 cell grid (1 km resolution) Bottom elevation for each cell is truncated beyond 100 m 27

Temperature 28

Chlorophyll-a (mg/m 3, sqr-transformed) 29

Dissolved Oxygen 2 0 0 1 June 15th July 16th August 16th 2 0 0 2 2 0 1 0 30

Direct Effects of Low DO Exposure-effects sub-models (Neilan and Rose 2014) Estimated from experiments (Thomas and Rahman 2012, Rahman and Thomas 2012) Only imposed on late juveniles, age-1, and age-2 31

Avoidance (July 16 th ) DO (mg/l) Abundance [ln(fish / 10 km 2 )] 2002 Severe Baseline 32

25% Reduced Nutrient Loadings

Example 4: Red Snapper Campbell, M.D., K.A. Rose, K. Boswell, and J.H. Cowan. 2011. Ecological Modelling 222:3895-3909. 34

Introduction Coastal Louisiana Habitats Petroleum Platforms Artificial Reef Communities Construction/Deconstruction Dismantling unused oil rigs could boost Louisiana's artificial reef program By Richard Thompson, Times-Picayune Sunday, October 24, 2010

What is the effect of increasing the number and spacing of artificial reefs on: Species movement patterns Species abundance and productivity Prey densities around platform halo effect

Spatial Grid 90 80 70 Designate Habitat 90 x 90 cells, 324 km 2 Each cell is 4000 m 2 Cells are rig or benthic Prey Distribution East - West 5 prey types: copepods, shrimp, crabs, pelagic fish, and benthic fish Prey population on each cell updated hourly with logistic South - North 60 50 40 30 20 0 0 10 20 30 40 50 60 70 80 90 28 26 Temperature Assumed to be constant across the grid Function of calendar day Jan Mar May Jul Sep Nov Jan 10 Degrees Celcius 24 22 20 18 16 14 12

Fish Community and Species Types Primary Community: Red snapper, pinfish, Atlantic croaker Movement, consumption, growth Mortality and recruitment Competitor and Predator: Bluefish Movement, consumption, and predation Influence on primary community Predator Only: Jack spp. Movement and predation Influence on primary community Photos courtesy of - http://floridasportfishing.com * Not to scale

10000 8000 South - North 6000 4000 2000 0 0 2000 4000 6000 8000 10000 East - West Hourly positions during four days in year 20 of a 16 AR simulation red snapper (red), pinfish (green), Atlantic croaker (light blue), bluefish (blue), jack-like species (black)

Insights? Capabilities for assessing habitat effects on upper trophic level dynamics seems: Limited Stalled: from capacity to abundance Behavioral movement drives the results

Insights? Integration of spatial and temporal scales across variables and linking to processes appears arbitrary We confuse inputs and emergent outputs? Rule or random walk based approaches are inputs Without considering the energetics and other costs of altered movements, we show that the code works

Insights? Decision-making Adaptive Costs Model coupling Validation data Watkins and Rose. 2013.