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State of the Ecosystem Structure
Proposed 2023

SOE January Synthesis Meeting
18-19 January 2023

Sarah Gaichas, Kimberly Bastille, Geret DePiper, Kimberly Hyde, Scott Large, Sean Lucey, Laurel Smith
Northeast Fisheries Science Center
and all SOE contributors

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State of the Ecosystem (SOE) reporting

Improving ecosystem information and synthesis for fishery managers

  • Ecosystem indicators linked to management objectives (DePiper, et al., 2017)

    • Contextual information
    • Report evolving since 2016
    • Fishery-relevant subset of full Ecosystem Status Reports
  • Open science emphasis (Bastille, et al., 2020)

  • Used within Mid-Atlantic Fishery Management Council's Ecosystem Process (Muffley, et al., 2020)

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State of the Ecosystem: Maintain 2021-2022 structure for 2023

2023 Report Structure

  1. Graphical summary
    • Page 1 report card re: objectives →
    • Page 2 risk summary bullets
    • Page 3 synthesis themes
  2. Performance relative to management objectives
  3. Risks to meeting management objectives
Ecosystem-scale fishery management objectives
Objective Categories Indicators reported
Provisioning and Cultural Services
Seafood Production Landings; commercial total and by feeding guild; recreational harvest
Profits Revenue decomposed to price and volume
Recreation Angler trips; recreational fleet diversity
Stability Diversity indices (fishery and ecosystem)
Social & Cultural Community engagement/reliance and environmental justice status
Protected Species Bycatch; population (adult and juvenile) numbers, mortalities
Supporting and Regulating Services
Biomass Biomass or abundance by feeding guild from surveys
Productivity Condition and recruitment of managed species, primary productivity
Trophic structure Relative biomass of feeding guilds, zooplankton
Habitat Estuarine and offshore habitat conditions
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State of the Ecosystem report structure: graphical summary (showing 2022)

State of the Ecosystem page 1 summary table

State of the Ecosystem page 2 risk bullets

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Ecosystem synthesis themes

Characterizing ecosystem change for fishery management

  • Societal, biological, physical and chemical factors comprise the multiple system drivers that influence marine ecosystems through a variety of different pathways.
  • Changes in the multiple drivers can lead to regime shifts — large, abrupt and persistent changes in the structure and function of an ecosystem.
  • Regime shifts and changes in how the multiple system drivers interact can result in ecosystem reorganization as species and humans respond and adapt to the new environment.

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State of the Ecosystem report scale and figures

Spatial scale NEFSC survey strata used to calculate Ecosystem Production Unit biomass

A glossary of terms (2021 Memo 5), detailed technical methods documentation and indicator data are available online.

Key to figures

Trends assessed only for 30+ years: more information

Orange line = significant increase

Purple line = significant decrease

No color line = not significant or < 30 years

Grey background = last 10 years

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2023 State of the Ecosystem Request tracking memo SARAH STILL TO UPDATE

Request Year Source Status Progress Memo Section
Add "This report is for [audience]" 2021 MAFMC SSC In SOE Introduction section 1
State management objectives first in report 2021 NEFMC In SOE Introduction section + Table 2
Ocean acidification (OA) in NEFMC SOE 2021 NEFMC SSC In SOE Climate risks section 3
Habitat impact of fishing based on gear. 2021 NEFMC In SOE Habitat risks section 4
Revisit right whale language 2021 NEFMC In SOE Protected species section 5
Sum of TAC/ Landings relative to TAC 2021 MAFMC SSC In SOE-MAFMC Seafood production section 6
Estuarine Water Quality 2020 NEFMC In SOE-MAFMC, In progress-NEFMC Climate and Habitat Risks sections MAFMC; Intern collated New England NERRS data 7
More direct opportunities for feedback 2021 MAFMC SSC In progress MAFMC SSC ecosystem subgroup 8
Further definition of regime shift 2021 MAFMC SSC In progress Regime shift analyses for specific indicators define "abrupt" and "persistent" quantitatively 9
Expand collaboration with Canadian counterparts 2021 MAFMC SSC In progress Currently drafting a NMFS-DFO climate/fisheries collaboration framework. 10
Fall turnover date index 2021 MAFMC SSC In progress See Current Conditions report 11
Links between species availability inshore/offshore (estuarine conditions) and trends in recreational fishing effort? 2021 MAFMC In progress Bluefish prey index inshore/offshore partially addresses 12
Apex predator index (pinnipeds) 2021 NEFMC In progress Protected species branch developing time series 13
Forage availability index (Herring/Sandlance) 2021 NEFMC In progress Bluefish prey index partially addresses 14
Fishery gear modifications accounted for in shark CPUE? 2021 MAFMC In progress Updated methods in tech-doc 15
Trend analysis 2021 NEFMC SSC In progress Evaluating empirical thresholds 16
Regime shifts in Social-Economic indicators 2021 NEFMC SSC In progress National working group and regional study 17
Linking Condition 2020 MAFMC In progress Not ready for 2022 18
Cumulative weather index 2020 MAFMC In progress Data gathered for prototype 19
VAST and uncertainty 2020 Both Councils In progress Not ready for 2022 20
Seal index 2020 MAFMC In progress Not ready for 2022 21
Breakpoints 2020 NEFMC In progress Evaluating empirical thresholds 22
Management complexity 2019 MAFMC In progress Student work needs further analysis, no further work this year 23
Shellfish growth/distribution linked to climate (system productivity) 2019 MAFMC In progress Project with A. Hollander 24
Avg weight of diet components by feeding group 2019 Internal In progress Part of fish condition project 25
Mean stomach weight across feeding guilds 2019 MAFMC In progress Intern evaluated trends in guild diets 26
Inflection points for indicators 2019 Both Councils In progress Evaluating empirical thresholds 27
Recreational bycatch mortality as an indicator of regulatory waste 2021 MAFMC SSC Not started Lacking resources this year 28
Sturgeon Bycatch 2021 MAFMC SSC Not started Lacking resources this year 29
Decomposition of diversity drivers highlighting social components 2021 MAFMC SSC Not started Lacking resources this year 30
Changing per capita seafood consumption as driver of revenue? 2021 MAFMC Not started Lacking resources this year 31
Nutrient input, Benthic Flux and POC(particulate organic carbon ) to inform benthic productivity by something other than surface indidcators 2021 MAFMC SSC Not started Lacking resources this year 32
Relate OA to nutrient input; are there "dead zones" (hypoxia)? 2021 MAFMC Not started Lacking resources this year 33
Indicators of chemical pollution in offshore waters 2021 MAFMC Not started Lacking resources this year 34
How does phyto size comp affect EOF indicator, if at all? 2021 MAFMC Not started May pursue with MAFMC SSC eco WG 35
Indicator of scallop pred pops poorly sampled by bottom trawls 2021 NEFMC Not started Lacking resources this year 36
Compare EOF (Link) thresholds to empirical thresholds (Large, Tam) 2021 MAFMC SSC Not started May pursue with MAFMC SSC eco WG 37
Time series analysis (Zooplankton/Forage fish) to tie into regime shifts 2021 MAFMC SSC Not started Lacking resources this year 38
Optimum yield for ecosystem 2021 NEFMC Not started May pursue with MAFMC SSC eco WG 39
Re-evaluate EPUs 2020 NEFMC Not started Lacking resources this year 40
Incorporate social sciences survey from council 2020 NEFMC Not started Lacking resources this year 41
Biomass of spp not included in BTS 2020 MAFMC Not started Lacking resources this year 42
Reduce indicator dimensionality with multivariate statistics 2020 NEFMC Not started Lacking resources this year 43
Estuarine condition relative to power plants and temp 2019 MAFMC Not started Lacking resources this year 44
Young of Year index from multiple surveys 2019 MAFMC Not started Lacking resources this year 45
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Report structure revised in 2021 to address Council requests and improve synthesis

  • Performance relative to management objectives
    • What does the indicator say--up, down, stable?
    • Why do we think it is changing: integrates synthesis themes
      • Multiple drivers
      • Regime shifts
      • Ecosystem reorganization
  • Objectives
    • Seafood production
    • Profits
    • Recreational opportunities
    • Stability
    • Social and cultural
    • Protected species
  • Risks to meeting fishery management objectives
    • What does the indicator say--up, down, stable?
    • Why this is important to managers: integrates synthesis themes
      • Multiple drivers
      • Regime shifts
      • Ecosystem reorganization
  • Risk categories
    • Climate: warming, ocean currents, acidification
      • Habitat changes (incl. vulnerability analysis)
      • Productivity changes (system and fish)
      • Species interaction changes
      • Community structure changes
    • Other ocean uses
      • Offshore wind development
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State of the Ecosystem Summary 2022:

Performance relative to management objectives

Seafood production decreasing arrow icon, status not evaluated

Profits decreasing arrow icon, status not evaluated

Recreational opportunities: Effort increasing arrow icon above average icon icon; Effort diversity decreasing arrow icon below average icon icon

Stability: Fishery no trend icon near average icon icon; Ecological mixed trend icon near average icon icon

Social and cultural, trend not evaluated, status of:

  • Fishing engagement and reliance by community
  • Environmental Justice (EJ) Vulnerability by community

Protected species:

  • Maintain bycatch below thresholds mixed trend icon meeting objectives icon
  • Recover endangered populations (NARW) decreasing arrow icon below average icon icon
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State of the Ecosystem Summary 2022:

Risks to meeting fishery management objectives

Climate: warming and changing oceanography continue

  • Heat waves and Gulf Stream instability
  • Estuarine, coastal, and offshore habitats affected, with range of species responses
  • Below average summer 2021 phytoplankton
  • Multiple fish with poor condition, declining productivity

Other ocean uses: offshore wind development

  • Current revenue in proposed areas
    • 1-31% by port (some with EJ concerns)
    • 0-20% by managed species
  • Different development impacts for species preferring soft bottom vs. hard bottom
  • Overlap with one of the only known right whale foraging habitats, increased vessel strike and noise risks
  • Rapid buildout in patchwork of areas
  • Scientific survey mitigation required
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2023 Performance relative to management objectives

Fishing icon made by EDAB       Fishing industry icon made by EDAB       Multiple drivers icon made by EDAB       Spiritual cultural icon made by EDAB       Protected species icon made by EDAB

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Objective: Mid Atlantic Seafood production decreasing arrow icon below average icon icon   Risk elements: ComFood and RecFood, unchanged

Indicator: Commercial landings

Key: Black = Landings of all species combined;

Red = Landings of MAFMC managed species

Indicators: Recreational harvest

Multiple potential drivers of landings changes: ecosystem and stock production, management actions, market conditions (including COVID-19 disruptions), and environmental change.

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The long-term declining trend in landings didn't change.

Mid Atlantic Landings drivers: Stock status? TAC?   Risk elements: Fstatus, Bstatus, MgtControl

Indicator: Stock status

Most stocks have good status. Butterfish B status has improved. Results from Dec 2022 Research Track assessments shown for Spiny dogfish (F above threshold) and bluefish (B above limit) do not represent official management advice.

Indicators: Total ABC or ACL, and Realized catch relative to management target

Few managed species have binding limits; Management less likely playing a role

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Stock status affects catch limits established by the Council, which in turn may affect landings trends. Summed across all MAFMC managed species, total Acceptable Biological Catch or Annual Catch Limits (ABC or ACL) have been relatively stable 2012-2020 (top). With the addition of blueline tilefish management in 2017, an additional ABC and ACL contribute to the total 2017-2020. Discounting blueline tilefish, the recent total ABC or ACL is lower relative to 2012-2013, with much of that decrease due to declining Atlantic mackerel ABC.

Nevertheless, the percentage caught for each stock’s ABC/ACL suggests that these catch limits are not generally constraining as most species are well below the 1/1 ratio (bottom). Therefore, stock status and associated management constraints are unlikely to be driving decreased landings for the majority of species.

Implications: Mid Atlantic Seafood Production Drivers

Biomass does not appear to drive landings trends

Key: Black = NEFSC survey;

Red = NEAMAP survey

  • Declining managed benthos, aggregate planktivores

  • Recreational drivers differ: shark fishery management, possibly survey methodology

Monitor:

  • climate risks including warming, ocean acidification, and shifting distributions

  • ecosystem composition and production changes

  • fishing engagement
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Because stock status is mostly acceptable, ABCs don't appear to be constraining for many stocks, and aggregate biomass trends appear stable, the decline in commercial landings is most likely driven by market dynamics affecting the landings of surfclams and ocean quahogs, as quotas are not binding for these species.

Climate change also seems to be shifting the distribution of surfclams and ocean quahogs, resulting in areas with overlapping distributions and increased mixed landings. Given the regulations governing mixed landings, this could become problematic in the future and is currently being evaluated by the Council.

Objective: New England Seafood production decreasing arrow icon below average icon icon

Indicators: Commercial landings

Key: Black = Landings of all species combined;

Red = Landings of NEFMC managed species

Indicators: Recreational harvest

Multiple drivers: ecosystem and stock production, management, market conditions (including COVID-19 disruptions), and environmental change

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Although scallop decreases are partially explained by a decreased TAC, analyses suggest that the drop in landings is at least partially due to market disruptions due to the COVID-19 pandemic. However, we do not anticipate the long-term declining trend in landings to change.

New England Landings drivers: Stock status? Survey biomass?

Indicator: Stock status

Stocks below BMSY increased from 8 to 9, stocks below ½ BMSY decreased from 6 to 4. Spiny dogfish results from RT are unofficial. Management still likely playing large role in seafood declines

Indicator: Survey biomass

Biomass availability still seems unlikely driver

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New indicators for 2023: New England Realized catch compared to specified catch

Implications: Discuss

  • Limited data for 2021
  • Most species with catch > management target from Multispecies FMP
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Implications: New England Seafood Production

Drivers:

  • decline in commercial landings is most likely driven by the requirement to rebuild individual stocks as well as market dynamics
  • other drivers affecting recreational landings: shark fishery management, possibly survey methodology

Monitor:

  • climate risks including warming, ocean acidification, and shifting distributions
  • ecosystem composition and production changes
  • fishing engagement

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Objective: Mid Atlantic Commercial Profits decreasing arrow icon below average icon icon   Risk element: CommRev, unchanged

Indicator: Commercial Revenue

Key: Black = Revenue of all species combined;

Red = Revenue of MAFMC managed species

Recent change driven by benthos
Monitor changes in climate and landings drivers:
  • Climate risk element: Surfclams and ocean quahogs are sensitive to ocean warming and acidification.
  • pH in surfclam summer habitat is approaching, but not yet at, pH affecting surfclam growth

Indicator: Bennet--price and volume indices

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Recent declines in prices contributed to falling revenue as quantities landed did not increase enough to counteract declining prices.

Indicator: Commercial Revenue

Key: Black = Revenue of all species combined;

Red = Revenue of NEFMC managed species

Both regions driven by single species

  • GOM high revenue despite low volume
  • Fluctuations in GB due to rotational management

Monitor changes in climate and landings drivers:

  • Sea scallops and lobsters are sensitive to ocean warming and acidification

Indicator: Bennet--price and volume indices

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Objective: Mid Atlantic Recreational opportunities no trend icon above average icon icon; decreasing arrow icon below average icon icon Risk element: RecValue, decreased risk; add diversity?

Indicators: Recreational effort and fleet diversity

Implications

  • Increased angler trips in 2020 relative to previous years strongly influenced the previously reported long term increase in recreational effort. Adding 2021 data, recreational effort (angler trips) has no long term trend.
  • The increasing long term trend from 2021 changed the risk categories for the RecValue element to low-moderate (previously ranked high risk). No trend indicates low risk.
  • Decline in recreational fleet diversity suggests a potentially reduced range of opportunities.
  • Driven by party/charter contraction and a shift toward shore based angling.
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Changes in recreational fleet diversity can be considered when managers seek options to maintain recreational opportunities. Shore anglers will have access to different species than vessel-based anglers, and when the same species, typically smaller fish. Many states have developed shore-based regulations where the minimum size is lower than in other areas and sectors to maintain opportunities in the shore angling sector.

Objective: New England Recreational opportunities no trend icon near average icon icon

Indicators: Recreational effort and fleet diversity

Implications

  • Absence of a long-term trend in recreational effort suggests relative stability in the overall number of recreational opportunities in New England
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Objective: Mid Atlantic Environmental Justice and Social Vulnerability   Risk element: Social

Indicators: Environmental justice vulnerability, commercial fishery engagement and reliance

Mid-Atlantic commercial fishing communities

Implications: Highlighted communities may be vulnerable to changes in fishing patterns due to regulations and/or climate change. When also experiencing environmental justice issues, they may have lower ability to successfully respond to change.

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These plots provide a snapshot of the presence of environmental justice issues in the most highly engaged and most highly reliant commercial and recreational fishing communities in the Mid-Atlantic. These communities may be vulnerable to changes in fishing patterns due to regulations and/or climate change. When any of these communities are also experiencing social vulnerability including environmental justice issues, they may have lower ability to successfully respond to change.

Objective: Mid Atlantic Environmental Justice and Social Vulnerability   Risk element: Social

Indicators: Environmental justice vulnerability, recreational fishery engagement and reliance

Mid-Atlantic recreational fishing communities

Implications: Highlighted communities may be vulnerable to changes in fishing patterns due to regulations and/or climate change. When also experiencing environmental justice issues, they may have lower ability to successfully respond to change.

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Objective: New England Environmental Justice and Social Vulnerability

Indicators: Environmental justice vulnerability, commercial fishery engagement and reliance

New England commercial fishing communities

Implications: Highlighted communities may be vulnerable to changes in fishing patterns due to regulations and/or climate change. When also experiencing environmental justice issues, they may have lower ability to successfully respond to change.

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These plots provide a snapshot of the presence of environmental justice issues in the most highly engaged and most highly reliant commercial and recreational fishing communities in the Mid-Atlantic. These communities may be vulnerable to changes in fishing patterns due to regulations and/or climate change. When any of these communities are also experiencing social vulnerability including environmental justice issues, they may have lower ability to successfully respond to change.

Objective: New England Environmental Justice and Social Vulnerability

Indicators: Environmental justice vulnerability, recreational fishery engagement and reliance

New England recreational fishing communities

Implications: Highlighted communities may be vulnerable to changes in fishing patterns due to regulations and/or climate change. When also experiencing environmental justice issues, they may have lower ability to successfully respond to change.

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Objective: Mid Atlantic Fishery Stability no trend icon near average icon icon   Risk elements: FishRes1 and FleetDiv, unchanged

Fishery Indicators: Commercial fleet count, fleet diversity

Most recent fleet counts at low range of series

Fishery Indicators: commercial species revenue diversity, recreational species catch diversity

Most recent near series low value. Covid role?

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Ecological Indicators: zooplankton and larval fish diversity

Ecological Indicator: expected number of species, NEFSC bottom trawl survey

Implications:

  • stable capacity to respond to the current range of commercial fishing opportunities
  • recreational catch diversity maintained by a different set of species over time
  • monitor zooplankton diversity driven by declining dominant species
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While larval and adult fish diversity indices are stable, a few warm-southern larval species are becoming more dominant. Increasing zooplankton diversity is driven by declining dominance of an important species, which warrants continued monitoring.

Objective: New England Fishery Stability decreasing arrow icon Com below average icon icon; Rec near average icon icon

Fishery Indicators: Commercial fleet count, fleet diversity

Most recent around lowest points in series

Fishery Indicators: commerical species revenue diversity, recreational species catch diversity

Most recent lowest point in series. Covid role?

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Ecological Indicators: zooplankton and larval fish diversity

Ecological Indicator: expected number of species, NEFSC bottom trawl survey

Implications:

  • Commercial fishery diversity driven by small number of species
  • Diminished capacity to respond to future fishing opportunities
  • Recreational diversity due to species distributions and regulations
  • Adult diversity in GOM suggests increase in warm-water species
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  • Overall stability in the fisheries and ecosystem components
  • Increasing diversity in several indicators warrants continued monitoring

Indicators: Harbor porpoise and gray seal bycatch

Implications:

  • Currently meeting objectives

  • Risk element: TechInteract, evaluated by species and sector: 14 low, 6 low-mod, 3 mod-high risk, unchanged

  • The downward trend in harbor porpoise bycatch can also be due to a decrease in harbor porpoise abundance in US waters, reducing their overlap with fisheries, and a decrease in gillnet effort.

  • The increasing trend in gray seal bycatch may be related to an increase in the gray seal population (U.S. pup counts).

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Objectives: All Areas Protected species Recover endangered populations decreasing arrow icon below average icon icon

Indicators: North Atlantic right whale population, calf counts

Implications:

  • Population drivers for North Atlantic Right Whales (NARW) include combined fishery interactions/ship strikes, distribution shifts, and copepod availability.

  • Additional potential stressors include offshore wind development, which overlaps with important habitat areas used year-round by right whales, including mother and calf migration corridors and foraging habitat.

  • Unusual mortality events continue for 3 large whale species.

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2023 Risks to meeting fishery management objectives

Climate icon made by EDAB       Wind icon made by EDAB

Hydrography icon made by EDAB       Phytoplankon icon made by EDAB       Forage fish icon made by EDAB       Apex predators icon made by EDAB       Other human uses icon made by EDAB

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Risks: Climate change Mid Atlantic

Indicators: ocean currents, bottom and surface temperature, detrended marine heatwaves

 
 
     
 
 
   
 
   
   
 
   
 

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A marine heatwave is a warming event that lasts for five or more days with sea surface temperatures above the 90th percentile of the historical daily climatology (1982-2011).

Risks: Climate change Mid Atlantic, new bottom temperature indicators

In contrast to SST, long term BT is increasing in winter as well as other seasons

Heatwaves in bottom temperature last longer and happen later in the season than surface heatwaves. No consistent long term annual trend in bottom or surface heatwaves.

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Risks: Climate change Mid Atlantic, new seasonal transition indicators

Mid Atlantic

Coastwide

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Risks: Climate change New England

Indicators: ocean currents, bottom and surface temperature

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Risks: Climate change New England

Indicators: detrended marine heatwaves

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Risks: Climate change New England, new bottom temperature indicators

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Risks: Climate change New England, bottom heatwaves cont'd + new seasonal transition indicators

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Risks: Climate change and estuarine habitat   Risk element: EstHabitat 11 low, 4 high risk species

Indicators: Chesapeake Bay temperature and salinity

Indicator: SAV trends in Chesapeake Bay

Indicator: Water quality attainment

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Risks: Climate change and offshore habitat

Indicator: cold pool indices

Indicator: Mid Atlantic Ocean acidification Mid Seasonal pH

Indicator: warm core rings

Indicator: New England Ocean acidification NE Seasonal pH

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Risks: Ecosystem productivity Mid Atlantic   Risk element: EcoProd

Indicators: chlorophyll, primary production, zooplankton

Implications: increased production by smaller phytoplankton implies less efficient transfer of primary production to higher trophic levels. Monitor implications of increasing gelatinous zooplankton and krill.

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Below average phytoplankton biomass could be due to reduced nutrient flow to the surface and/or increased grazing pressure. A short fall bloom was detected in November. Primary productivity (the rate of photosynthesis) was average to below average throughout 2021

Risks: Ecosystem productivity Mid Atlantic   Risk element: EcoProd

Indicator: fish condition

Indicator: fish productivity anomaly

Implications: Species in the MAB had mixed condition in 2022. Survey-based fish productivity continues a general decline. Update? Preliminary results of synthetic analyses show that changes in temperature, zooplankton, fishing pressure, and population size influence the condition of different fish species.

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Risks: Ecosystem productivity New England

Indicators: chlorophyll, primary production

Implications: increased production by smaller phytoplankton implies less efficient transfer of primary production to higher trophic levels. Monitor implications of increasing gelatinous zooplankton and krill.

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Below average phytoplankton biomass could be due to reduced nutrient flow to the surface and/or increased grazing pressure. A short fall bloom was detected in November. Primary productivity (the rate of photosynthesis) was average to below average throughout 2021

Risks: Ecosystem productivity New England

Indicator: fish condition

Georges Bank

Gulf of Maine

Implications: Many species in New England showed improved condition in 2021-2022. Preliminary results of synthetic analyses show that changes in temperature, zooplankton, fishing pressure, and population size influence the condition of different fish species.

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Risks: Ecosystem productivity New England

Indicator: fish productivity anomaly

Small fish per large fish biomass anomaly on Georges Bank. The summed anomaly across species is shown by the black line.

Small fish per large fish biomass anomaly on Georges Bank. The summed anomaly across species is shown by the black line.

Small fish per large fish biomass anomaly in the Gulf of Maine. The summed anomaly across species is shown by the black line.

Small fish per large fish biomass anomaly in the Gulf of Maine. The summed anomaly across species is shown by the black line.

Survey based fish productivity shows no clear trend in New England.

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Risks: Ecosystem productivity, new fish productivity anomaly based on stock assessments

Mid Atlantic region stocks

New England region stocks

Methods from (Perretti, et al., 2017). Black line indicates sum where there are the same number of assessments across years.

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Risks: Ecosystem productivity All regions

Implications: fluctuating environmental conditions and prey for forage species affect both abundance and energy content. Energy content varies by season, and has changed over time most dramatically for Atlantic herring

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Risks: Ecosystem structure All regions

Indicators: distribution shifts, diversity (previous sections) predator status and trends here

No trend in aggregate sharks

  • No obvious increase in shark populations
  • Most highly migratory fish predators are not depleted:
    • 10 above B target
    • 7 above B limit but below B target
    • 2 below B limit

HMS populations mainly at or above target

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Risks: Ecosystem structure New England

Indicators: predators

Gray seals increasing

  • Breeding season ~ 27,000 US gray seals, Canada's population ~ 425,000 (2016)
  • Canada's population increasing at ~ 4% per year
  • U.S. pupping sites increased from 1 (1988) to 9 (2019)
  • Harbor and gray seals are generalist predators that consume more than 30 different prey species: red, white and silver hake, sand lance, yellowtail flounder, four-spotted flounder, Gulf-stream flounder, haddock, herring, redfish, and squids.

Implications: stable predator populations suggest stable predation pressure on managed species, but increasing predator populations may reflect increasing predation pressure.

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Risks: Ecosystem structure New England

Common tern productivity decline reflecting prey, other drivers? Discuss

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Risks: Ecosystem structure: new diet based forage fish index

Mid Atlantic

New England

Is the forage base changing over time?

VAST model using 22 predators to sample 20 forage fish groups, includes more unmanaged forage (anchovies, sandlance) than direct survey trawl data.

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Risks: Habitat climate vulnerability   New, opportunity to refine habitat risks

Indicators: climate sensitive species life stages mapped to climate vulnerable habitats

See MAFMC 2022 EAFM risk assessment for example species narratives

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Risks: Habitat: new habitat diversity trend indicators

Implications: discuss

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Implications: Climate change and managed species   Risk elements unchanged, new info:

Climate: 6 low, 3 low-mod, 4 mod-high, 1 high risk

Multiple drivers with different impacts by species

  • Seasonal estuarine conditions affect life stages of striped bass, blue crabs, summer flounder, black sea bass differently
    • Chesapeake summer hypoxia, temperature better than in past years, but worse in fall
    • Habitat improving in some areas (tidal fresh SAV, oyster reefs), but eelgrass declining
  • Ocean acidification impact on vulnerable surfclams
    • Areas of low pH identified in surfclam and scallop habitat
    • Lab work identified pH thresholds for surfclam growth
  • Warm core rings important to Illex availability. Fishing effort concentrates on the eastern edge of warm core rings, where upwelling and enhanced productivity ocurr

DistShift: 2 low, 9 mod-high, 3 high risk species

Shifting species distributions alter both species interactions, fishery interactions, and expected management outcomes from spatial allocations and bycatch measures based on historical fish and protected species distributions.

New Indicator: protected species shifts

]
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Risks: Offshore Wind Development Mid Atlantic   Element: OceanUse

Indicators: development timeline, fishery and community specific revenue in lease areas

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Risks: Offshore Wind Development New England

Indicators: fishery and community specific revenue in lease areas

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Risks: Offshore Wind Development Summary

Implications: revise

  • X% of port revenue from fisheries currently comes from areas proposed for offshore wind development. Some communities have environmental justice concerns and gentrification vulnerability.
  • Up to Y% of annual commercial landings and revenue for Mid-Atlantic species occur in lease areas.
  • Development will affect species differently, negatively affecting species that prefer soft bottom habitat while potentially benefiting species that prefer hard structured habitat.
  • Planned wind areas overlap with one of the only known right whale foraging habitats, and altered local oceanography could affect right whale prey availability. Development also brings increased vessel strike risk and the potential impacts of pile driving noise.
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Current plans for rapid buildout of offshore wind in a patchwork of areas spreads the impacts differentially throughout the region Evaluating the impacts to scientific surveys has begun.

THANK YOU! SOEs made possible by (at least) 61 contributors from 14 institutions UPDATE THIS!

Kimberly Bastille
Aaron Beaver (Anchor QEA)
Andy Beet
Ruth Boettcher (Virginia Department of Game and Inland Fisheries)
Mandy Bromilow (NOAA Chesapeake Bay Office)
Zhuomin Chen (Woods Hole Oceanographic Institution)
Joseph Caracappa
Doug Christel (GARFO)
Patricia Clay
Lisa Colburn
Jennifer Cudney (NMFS Atlantic HMS Management Division)
Tobey Curtis (NMFS Atlantic HMS Management Division)
Geret DePiper
Dan Dorfman (NOAA-NOS-NCCOS)
Hubert du Pontavice
Emily Farr (NMFS Office of Habitat Conservation)
Michael Fogarty
Paula Fratantoni
Kevin Friedland
Marjy Friedrichs (VIMS)
Sarah Gaichas
Ben Galuardi (GARFO)
Avijit Gangopadhyay (School for Marine Science and Technology, University of Massachusetts Dartmouth)
James Gartland (Virginia Institute of Marine Science)
Glen Gawarkiewicz (Woods Hole Oceanographic Institution)
Sean Hardison
Kimberly Hyde
John Kosik
Steve Kress (National Audubon Society’s Seabird Restoration Program)
Young-Oh Kwon (Woods Hole Oceanographic Institution)

Scott Large
Andrew Lipsky
Sean Lucey
Don Lyons (National Audubon Society’s Seabird Restoration Program)
Chris Melrose
Shannon Meseck
Ryan Morse
Brandon Muffley (MAFMC)
Kimberly Murray
Chris Orphanides
Richard Pace
Tom Parham (Maryland DNR)
Charles Perretti
CJ Pellerin (NOAA Chesapeake Bay Office)
Grace Roskar (NMFS Office of Habitat Conservation)
Grace Saba (Rutgers)
Vincent Saba
Sarah Salois
Chris Schillaci (GARFO)
Dave Secor (CBL)
Angela Silva
Adrienne Silver (UMass/SMAST)
Emily Slesinger (Rutgers University)
Laurel Smith
Talya tenBrink (GARFO)
Bruce Vogt (NOAA Chesapeake Bay Office)
Ron Vogel (UMD Cooperative Institute for Satellite Earth System Studies and NOAA/NESDIS Center for Satellite Applications and Research)
John Walden
Harvey Walsh
Changhua Weng
Mark Wuenschel

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References

Bastille, K. et al. (2020). "Improving the IEA Approach Using Principles of Open Data Science". In: Coastal Management 0.0. Publisher: Taylor & Francis _ eprint: https://doi.org/10.1080/08920753.2021.1846155, pp. 1-18. ISSN: 0892-0753. DOI: 10.1080/08920753.2021.1846155. URL: https://doi.org/10.1080/08920753.2021.1846155 (visited on Dec. 09, 2020).

DePiper, G. S. et al. (2017). "Operationalizing integrated ecosystem assessments within a multidisciplinary team: lessons learned from a worked example". En. In: ICES Journal of Marine Science 74.8, pp. 2076-2086. ISSN: 1054-3139. DOI: 10.1093/icesjms/fsx038. URL: https://academic.oup.com/icesjms/article/74/8/2076/3094701 (visited on Mar. 09, 2018).

Muffley, B. et al. (2020). "There Is no I in EAFM Adapting Integrated Ecosystem Assessment for Mid-Atlantic Fisheries Management". In: Coastal Management 0.0. Publisher: Taylor & Francis _ eprint: https://doi.org/10.1080/08920753.2021.1846156, pp. 1-17. ISSN: 0892-0753. DOI: 10.1080/08920753.2021.1846156. URL: https://doi.org/10.1080/08920753.2021.1846156 (visited on Dec. 09, 2020).

Perretti, C. et al. (2017). "Regime shifts in fish recruitment on the Northeast US Continental Shelf". En. In: Marine Ecology Progress Series 574, pp. 1-11. ISSN: 0171-8630, 1616-1599. DOI: 10.3354/meps12183. URL: http://www.int-res.com/abstracts/meps/v574/p1-11/ (visited on Feb. 10, 2022).

Additional resources

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State of the Ecosystem (SOE) reporting

Improving ecosystem information and synthesis for fishery managers

  • Ecosystem indicators linked to management objectives (DePiper, et al., 2017)

    • Contextual information
    • Report evolving since 2016
    • Fishery-relevant subset of full Ecosystem Status Reports
  • Open science emphasis (Bastille, et al., 2020)

  • Used within Mid-Atlantic Fishery Management Council's Ecosystem Process (Muffley, et al., 2020)

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