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
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 |
Performance relative to management objectives
Seafood production , status not evaluated
Profits , status not evaluated
Recreational opportunities: Effort
; Effort diversity
Stability: Fishery
; Ecological
Social and cultural, trend not evaluated, status of:
Protected species:
Risks to meeting fishery management objectives
Climate: warming and changing oceanography continue
Other ocean uses: offshore wind development
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.
The long-term declining trend in landings didn't change.
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
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.
Biomass does not appear to drive landings trends
Key: Black = NEFSC survey;
Red = NEAMAP survey
Monitor:
climate risks including warming, ocean acidification, and shifting distributions
ecosystem composition and production changes
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.
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
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
Implications: Discuss
Drivers:
Monitor:
Indicator: Commercial Revenue
Key: Black = Revenue of all species combined;
Red = Revenue of MAFMC managed species
Indicator: Bennet--price and volume indices
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
Monitor changes in climate and landings drivers:
Indicator: Bennet--price and volume indices
Indicators: Recreational effort and fleet diversity
Implications
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.
Indicators: Recreational effort and fleet diversity
Implications
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.
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
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.
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.
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?
Ecological Indicators: zooplankton and larval fish diversity
Ecological Indicator: expected number of species, NEFSC bottom trawl survey
Implications:
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.
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?
Ecological Indicators: zooplankton and larval fish diversity
Ecological Indicator: expected number of species, NEFSC bottom trawl survey
Implications:
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).
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.
Indicators: ocean currents, bottom and surface temperature, detrended marine heatwaves
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).
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.
Mid Atlantic
Coastwide
Indicators: ocean currents, bottom and surface temperature
Indicators: detrended marine heatwaves
Indicators: Chesapeake Bay temperature and salinity
Indicator: SAV trends in Chesapeake Bay
Indicator: Water quality attainment
Indicator: cold pool indices
Indicator: Mid Atlantic Ocean acidification
Indicator: warm core rings
Indicator: New England Ocean acidification
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.
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
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.
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.
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.
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.
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
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.
Common tern productivity decline reflecting prey, other drivers? Discuss
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.
Indicators: climate sensitive species life stages mapped to climate vulnerable habitats
See MAFMC 2022 EAFM risk assessment for example species narratives
Implications: discuss
Climate: 6 low, 3 low-mod, 4 mod-high, 1 high risk
Multiple drivers with different impacts by species
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
Indicators: development timeline, fishery and community specific revenue in lease areas
Indicators: fishery and community specific revenue in lease areas
Implications: revise
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.
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).
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).
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
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