Ecosystem indicators linked to management objectives (DePiper, et al., 2017)
Open science emphasis (Bastille, et al., 2020)
The IEA Loop1
Objective Categories | Indicators reported here |
---|---|
Provisioning and Cultural Services | |
Seafood Production | Landings; commercial total and by feeding guild; recreational harvest |
Profits | Revenue decomposed to price and volume |
Recreation | Days fished; recreational fleet diversity |
Stability | Diversity indices (fishery and ecosystem) |
Social & Cultural | Community engagement/reliance 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 |
Request | Year | Source | Progress | Memo Section |
---|---|---|---|---|
Report card and summary visualizations | 2019 | Both Councils | SOE new report card table and summary visualizaitions of synthesis themes | 1 |
Ecosystem Overfishing indicators (Link and Watson, 2019) | 2020 | Both Councils | SOE two ecosystem overfishing indicators included | 2 |
Primary production required, interpretation of decline? | 2020 | Both Councils | SOE indicator reworked along with Link and Watson metrics | 3 |
Climate Change context | 2020 | NEFMC | SOE reorganized; Risks section added emphasizing climate change | 4 |
Clarify language (e.g., primary production required) | 2020 | Both Councils | SOE edited by Research Communications Branch; glossary included | 5 |
Copy Editing | 2020 | Both Councils | SOE edited by Research Communications Branch | 6 |
Ocean Acidification | 2020 | NEFMC | SOE indicator added with in-situ data linked to preliminary lab work on thresholds | 7 |
Include examples of High/Low engaged ports | 2020 | NEFMC | SOE indicator reworked to show individual ports and social vulnerability | 8 |
Expand wind lease area and habitat overlap | 2020 | MAFMC | SOE indicator expanded to rank species with habitat in wind lease areas by landings in wind lease areas | 9 |
Expand cold pool index | 2020 | MAFMC | SOE indicator expanded with modeled data to include area and other attributes | 10 |
Seperate Bigelow/Albatross catch diversity metric | 2020 | MAFMC | SOE indicator added | 11 |
Shark abundance and catch indicators | 2020 | MAFMC | SOE multiple shark indicators added | 12 |
Uncertainty estimates | 2020 | MAFMC | SOE included for subset of indicators | 13 |
Bycatch index | 2020 | NEFMC | SOE added seal bycatch indicator, retained harbor porpoise indicator | 14 |
Marine Mammal consumption | 2019 | MAFMC | SOE added discussion of seal diets, memo no new consumption ests since Smith et al but could be in the future once work is complete | 15 |
Estuarine Water Quality | 2020 | NEFMC | SOE Chesapeake indicators updated and expanded | 16 |
Forage abundance | 2019 | MAFMC | SOE forage anomaly indicator added | 17 |
Linking Condition | 2020 | MAFMC | in progress; not ready for 2021 | 18 |
Avg weight of diet components by feeding group | 2019 | Internal | in progress; part of fish condition | 19 |
Mean stomach weight across feeding guilds | 2019 | MAFMC | in progress; stomach fullness analysis started--species level | 20 |
Shellfish growth/distribution linked to climate (system productivity) | 2019 | MAFMC | in progress; project with R Mann student to start 2021 | 21 |
Cumulative weather index | 2020 | MAFMC | in progress; data gathered for prototype | 22 |
Management complexity | 2019 | MAFMC | in progress; student work needs further analysis, no further work in 2020 | 23 |
VAST and uncertainty | 2020 | Both Councils | in progress; not ready for 2021 | 24 |
Seal index | 2020 | MAFMC | in progress; not ready for 2021 | 25 |
Incorporate social sciences survey from council | 2020 | NEFMC | unable to start in 2020 | 26 |
Young of Year index from multiple surveys | 2019 | MAFMC | unable to start in 2020 | 27 |
Biomass of spp not included in BTS | 2020 | MAFMC | unable to start in 2020 | 28 |
Estuarine condition relative to power plants and temp | 2019 | MAFMC | unable to start in 2020 | 29 |
Inflection points for indicators | 2019 | Both Councils | unable to start in 2020 | 30 |
Reduce indicator dimensionality with multivariate statistics | 2020 | NEFMC | unable to start in 2020 | 31 |
Breakpoints | 2020 | NEFMC | unable to start in 2020 | 32 |
Re-evaluate EPUs | 2020 | NEFMC | unable to start in 2020 | 33 |
Characterizing ecosystem change for fishery management
Spatial scale
A glossary of terms (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
Indicators: Commercial landings
Key: Black = Landings of all species combined;
Red = Landings of NEFMC managed species
Recreational landings
Multiple drivers: ecosystem and stock production, management, market conditions, and environment
Key:
Orange background = Tipping point overfishing threshold, Link and Watson 2019
Green background = Optimal range, Link and Watson 2019
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:
Indicator: Commercial Revenue
Key: Black = Revenue of all species combined;
Red = Revenue of NEFMC managed species
Monitor changes in climate and landings drivers:
Indicator: Bennet--price and volume indices
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
Memo 22-23, Cumulative weather index and management complexity drivers under construction
Fishery Indicators: Commercial fleet count, fleet diversity
Fishery Indicators: commerical species revenue diversity, recreational species catch diversity
Ecological Indicators: zooplankton and larval fish diversity
Ecological Indicator: expected number of species, NEFSC bottom trawl survey (Memo 11)
Implications:
Indicators: Social vulnerability, fishery engagement and reliance
New England recreational fishing communities
New England commercial fishing communities
Implications: Highlighted 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, they may have lower ability to successfully respond to change. These indicators may also point to communities that are vulnerable to environmental justice issues.
Indicators: Harbor porpoise and gray seal bycatch (Memo 14)
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
Implications:
Population drivers for North Atlantic Right Whales (NARW) include combined fishery interactions/ship strikes, distribution shifts, and copepod availability.
Unusual mortality events continue for 3 large whale species, harbor and gray seals.
Indicators: ocean currents
Indicators: bottom temperatures
Indicators: marine heatwaves
Indicators: primary production
Indicators: 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.
Indicators: plankton-based forage anomaly and forage fish energy content (Memo 17)
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: fish condition (Memo 18)
Georges Bank
Gulf of Maine
Indicators: distribution shifts (slide 13), diversity (slide 17), predators (Memo 12, 15, 25)
Gray seals increasing
Implications: stable predator populations suggest stable predation pressure on managed species, but increasing predator populations may reflect increasing predation pressure.
Indicators: climate sensitive species life stages mapped to climate vulnerable habitats
Implications:
Current plans for rapid buildout of offshore wind in a patchwork of areas spreads the impacts differentially throughout the region
1-12% of total average revenue for major New England commerical species in lease areas could be displaced if all sites are developed. Displaced fishing effort can alter fishing methods, which can in turn change habitat, species (managed and protected), and fleet interactions.
Right whales may be displaced, and altered local oceanography could affect distribution of their zooplankton prey.
Scientific data collection surveys for ocean and ecosystem conditions, fish, and protected species will be altered, potentially increasing uncertainty for management decision making.
The New England and Mid-Atlantic SOEs made possible by (at least) 52 contributors from 10 institutions
Andy Beet
Kimberly Bastille
Ruth Boettcher (Virginia Department of Game and Inland Fisheries)
Mandy Bromilow (NOAA Chesapeake Bay Office)
Zhuomin Chen (Woods Hole Oceanographic Institute)
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
Emily Farr (NMFS Office of Habitat Conservation)
Michael Fogarty
Paula Fratantoni
Kevin Friedland
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 Institute)
Scott Large
Andrew Lipsky
Sean Lucey
Don Lyons (National Audubon Society’s Seabird Restoration Program)
Chris Melrose
Shannon Meseck
Ryan Morse
Kimberly Murray
Chris Orphanides
Richard Pace
Charles Perretti
CJ Pellerin (NOAA Chesapeake Bay Office)
Grace Roskar (NMFS Office of Habitat Conservation)
Grace Saba (Rutgers)
Vincent Saba
Chris Schillaci (GARFO)
Angela Silva
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).
Ecosystem indicators linked to management objectives (DePiper, et al., 2017)
Open science emphasis (Bastille, et al., 2020)
The IEA Loop1
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