Ecosystem indicators linked to management objectives (DePiper et al., 2017)
Open science emphasis (Bastille et al., 2020)
Used within Mid-Atlantic Fishery Management Council's Ecosystem Process (Muffley et al., 2020)
The IEA Loop1
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 |
Characterizing ecosystem change for fishery management
Spatial scale
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 yearsGrey background = last 10 years
Performance relative to management objectives - Georges Bank
Seafood production ,
Profits ,
Recreational opportunities: Effort ,
; Effort diversity
,
Stability: Fishery , Commercial
Rec
; Ecological
Social and cultural, trend not evaluated, status of:
Protected species:
Performance relative to management objectives - Gulf of Maine
Seafood production ,
Profits Total ,
; NEFMC Managed
,
Recreational opportunities: Effort ,
; Effort diversity
,
Stability: Fishery , Commercial
Rec
; Ecological
Social and cultural, trend not evaluated, status of:
Protected species:
Risks to meeting fishery management objectives
Climate: warming and changing oceanography continue
Risks to meeting fishery management objectives
Other ocean uses: offshore wind development
Indicators: Commercial landings
Key: Black = Landings of all species;
Blue = Seafood landings;
Red = NEFMC managed seafood landings
Indicators: Recreational harvest
Multiple potential drivers of landings changes: ecosystem and stock production, management actions, market conditions (including COVID-19 disruptions), and environmental change
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.
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
Drivers:
Monitor:
Indicator: Commercial Revenue
Key: Black = Revenue of all species combined;
Red = Revenue of NEFMC managed species
Indicator: Bennet--price and volume indices
Implications:
Both regions driven by single species
Monitor changes in climate and landings drivers:
Indicators: Recreational effort and fleet diversity
Implications:
Fishery Indicators: Commercial fleet count, fleet diversity
Fishery Indicators: Commercial species revenue diversity, recreational species catch diversity
Ecological Indicators: zooplankton and larval fish diversity
Ecological Indicator: expected number of species, NEFSC bottom trawl survey
Implications:
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.
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.
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.
Indicators: Harbor porpoise and gray seal bycatch
Implications:
Currently meeting objectives
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).
Indicators: North Atlantic right whale population, calf counts
Indicator: Gray seal pups
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 and 1 seal.
Indicators: bottom and surface temperature
Indicators: Extreme temperature events (detrended marine heatwaves)
A combination of long-term ocean warming and extreme events should be used to assess total heat stress on marine organisms.
Indicators: ocean currents
Implications: The Gulf Stream is trending north. This is associated with warmer ocean temperatures on the NE Shelf, higher proportion of Warm Slope Water in the Northeast Channel, and increased sea surface height.
Indicator: cold pool indices
Indicator: Ocean acidification
Indicator: warm core rings
2022 had the same number of warm core rings as 2021, but fewer near the continental shelf in 2022. Warm core ring near GB likely contributed to the marine heatwave and warm fall SST.
Summer aragonite saturation low for both Atlantic cods and American lobster in the Gulf of Maine.
Indicators: chlorophyll, primary production
Indicators: Phytoplankton, 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.
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
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.
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 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.
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
Indicator: Forage index
Indicator: Habitat model-based species richness by EPU
Implications: forage, including species not well sampled by bottom trawls, has been fluctuating over time. Richness calculated for the most common species suggests shifts away from the Mid Atlantic towards Georges Bank and Gulf of Maine.
Indicator: Common tern productivity
Common tern productivity decline reflecting prey, confounded by cold, wet wether in mid-to-late July when fledging occurs
Indicators: distribution shifts, diversity (previous sections) predator status and trends here
No trend in aggregate sharks
HMS populations mainly at or above target
Indicators: predators
Gray seals increasing
Implications: stable predator populations suggest stable predation pressure on managed species, but increasing predator populations may reflect increasing predation pressure.
New Indicator: protected species shifts
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.
Multiple drivers impact species differently
Seasonal estuarine conditions affect life stages of many federally-managed species
Climate change my shrink or fragment available habitat
Extreme temperature events happen intermittently, do not appear to be increasing in frequency, still contribute to overall thermal stress to organisms
Changes to cold pool affect species distribution, recruitment, and migration timing
31 offshore wind development projects are proposed
Indicators: fishery and community specific revenue in lease areas
Council request: which Mid-Atlantic ports have significant reliance on New England managed species?
Implications:
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.
Now organized by priority and category
Comments on priorities? Categories?
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
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).
Ecosystem indicators linked to management objectives (DePiper et al., 2017)
Open science emphasis (Bastille et al., 2020)
Used within Mid-Atlantic Fishery Management Council's Ecosystem Process (Muffley et al., 2020)
The IEA Loop1
Keyboard shortcuts
↑, ←, Pg Up, k | Go to previous slide |
↓, →, Pg Dn, Space, j | Go to next slide |
Home | Go to first slide |
End | Go to last slide |
Number + Return | Go to specific slide |
b / m / f | Toggle blackout / mirrored / fullscreen mode |
c | Clone slideshow |
p | Toggle presenter mode |
t | Restart the presentation timer |
?, h | Toggle this help |
Esc | Back to slideshow |