State of the Ecosystem 2023 Overview Mid-Atlantic and New England

class: right, middle, my-title, title-slide

.title[
# State of the Ecosystem 2023 Overview Mid-Atlantic and New England
]
.subtitle[
## NOAA Seminar 23 May 2023
]
.author[
### Sarah Gaichas, Kimberly Bastille, Sean Lucey, Geret DePiper, Kimberly Hyde, Scott Large, Laurel Smith Northeast Fisheries Science Center and all SOE contributors
]

---

class: top, left

## Goal: include climate and ecosystem information in management decision processes

.pull-left[
*Overview*
- What types of decisions are made?

* Single species catch limits
    * Allocations to fleets or areas
    * Coordination across boundaries and sectors 
    * Multispecies and ecosystem level tradeoffs

- How can ecosystem information support these decisions?

* Key tools: ecosystem reporting, risk assessment, scenario planning, managment strategy evaluation
    * Developing decision processes along with products

.footnote[
Word cloud based on [Mid-Atlantic Fishery Management Council EAFM Guidance Document](https://www.mafmc.org/s/EAFM-Doc-Revised-2019-02-08-palr.pdf)
]
]
.pull-right[
![:img EAFM Policy Guidance Doc Word Cloud](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/MAFMC_EAFMwordcloud.png)
]

---
## Background: Federal fishery management in the US

Eight regional Fishery Management Councils establish plans for sustainable management of stocks within their jurisdictions. All are governed by the same law, but tailor management to their regional stakeholder needs.
.center[
![:img US map highlighting regions for each fishery management council, 80%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/USCouncils.png)
] 
.footnote[
More information: http://www.fisherycouncils.org/  
https://www.fisheries.noaa.gov/topic/laws-policies#magnuson-stevens-act
]

---

# State of the Ecosystem (SOE) reporting
## Improving ecosystem information and synthesis for fishery managers

.pull-left-60[

- Ecosystem indicators linked to management objectives <a name=cite-depiper_operationalizing_2017></a>([DePiper, et al., 2017](https://academic.oup.com/icesjms/article/74/8/2076/3094701))
 + Contextual information
 + Report evolving since 2016
 + Fishery-relevant subset of full Ecosystem Status Reports

- Open science emphasis <a name=cite-bastille_improving_2021></a>([Bastille, et al., 2021](https://doi.org/10.1080/08920753.2021.1846155))

- Used within Mid-Atlantic Fishery Management Council's Ecosystem Process <a name=cite-muffley_there_2021></a>([Muffley, et al., 2021](https://doi.org/10.1080/08920753.2021.1846156))
 + Risk assessment <a name=cite-gaichas_implementing_2018></a>([Gaichas, et al., 2018](https://www.frontiersin.org/articles/10.3389/fmars.2018.00442/abstract))
 + Conceptual modeling <a name=cite-depiper_learning_2021></a>([DePiper, et al., 2021](https://doi.org/10.1093/icesjms/fsab054))
 + Management strategy evaluation ([MSE](https://www.mafmc.org/actions/summer-flounder-mse))

]

.pull-right-40[
*The IEA Loop1*
![IEA process from goal setting to assessment to strategy evaluation with feedbacks](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//iea-loop.png)

.footnote[
[1] https://www.integratedecosystemassessment.noaa.gov/national/IEA-approach
]
]
???

---
## State of the Ecosystem: Maintain 2021-2022 structure for 2023
.pull-left[

## 2023 Report Structure
1. Graphical summary
    + Page 1 report card re: objectives &rarr;
    + Page 2 risk summary bullets
    + Page 3 synthesis themes
1. Performance relative to management objectives
1. Risks to meeting management objectives

![:img State of the Ecosystem page 1 summary table, 50%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/SOE-MA-draft-03.16.23_Page_2.png)![:img State of the Ecosystem page 2 risk bullets, 50%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/SOE-MA-draft-03.16.23_Page_3.png)

]

.pull-right[

<table class="table" style="font-size: 14px; margin-left: auto; margin-right: auto;">
<caption style="font-size: initial !important;">Ecosystem-scale fishery management objectives</caption>
 <thead>
 <tr>
 <th style="text-align:left;font-weight: bold;"> Objective Categories </th>
 <th style="text-align:left;font-weight: bold;"> Indicators reported </th>
 </tr>
 </thead>
<tbody>
 <tr grouplength="6"><td colspan="2" style="border-bottom: 1px solid;">Provisioning and Cultural Services</td></tr>
<tr>
 <td style="text-align:left;padding-left: 2em;" indentlevel="1"> Seafood Production </td>
 <td style="text-align:left;"> Landings; commercial total and by feeding guild; recreational harvest </td>
 </tr>
 <tr>
 <td style="text-align:left;padding-left: 2em;" indentlevel="1"> Profits </td>
 <td style="text-align:left;"> Revenue decomposed to price and volume </td>
 </tr>
 <tr>
 <td style="text-align:left;padding-left: 2em;" indentlevel="1"> Recreation </td>
 <td style="text-align:left;"> Angler trips; recreational fleet diversity </td>
 </tr>
 <tr>
 <td style="text-align:left;padding-left: 2em;" indentlevel="1"> Stability </td>
 <td style="text-align:left;"> Diversity indices (fishery and ecosystem) </td>
 </tr>
 <tr>
 <td style="text-align:left;padding-left: 2em;" indentlevel="1"> Social &amp; Cultural </td>
 <td style="text-align:left;"> Community engagement/reliance and environmental justice status </td>
 </tr>
 <tr>
 <td style="text-align:left;padding-left: 2em;" indentlevel="1"> Protected Species </td>
 <td style="text-align:left;"> Bycatch; population (adult and juvenile) numbers, mortalities </td>
 </tr>
 <tr grouplength="4"><td colspan="2" style="border-bottom: 1px solid;">Supporting and Regulating Services</td></tr>
<tr>
 <td style="text-align:left;padding-left: 2em;" indentlevel="1"> Biomass </td>
 <td style="text-align:left;"> Biomass or abundance by feeding guild from surveys </td>
 </tr>
 <tr>
 <td style="text-align:left;padding-left: 2em;" indentlevel="1"> Productivity </td>
 <td style="text-align:left;"> Condition and recruitment of managed species, primary productivity </td>
 </tr>
 <tr>
 <td style="text-align:left;padding-left: 2em;" indentlevel="1"> Trophic structure </td>
 <td style="text-align:left;"> Relative biomass of feeding guilds, zooplankton </td>
 </tr>
 <tr>
 <td style="text-align:left;padding-left: 2em;" indentlevel="1"> Habitat </td>
 <td style="text-align:left;"> Estuarine and offshore habitat conditions </td>
 </tr>
</tbody>
</table>
]

---
## 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.

.pull-left[

![:img](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//SystemDrivers_v5.jpg)
]

.pull-right[
![:img](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//RegimeShift_V5.jpg)
]

---
## State of the Ecosystem report scale and figures

.pull-left[
Spatial scale
![:img NEFSC survey strata used to calculate Ecosystem Production Unit biomass, 80%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//EPU_Designations_Map.jpg)

A [glossary of terms](https://noaa-edab.github.io/tech-doc/glossary.html), detailed [technical methods documentation](https://NOAA-EDAB.github.io/tech-doc) and [indicator data](https://github.com/NOAA-EDAB/ecodata) are available online.  
]

.pull-right[
Key to figures
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-2-1.png" width="396" style="display: block; margin: auto;" />

.contrib[
Trends assessed only for 30+ years: [more information](https://noaa-edab.github.io/tech-doc/trend-analysis.html)

Orange line = significant increase
Purple line = significant decrease
No color line = not significant or < 30 years
Grey background = last 10 years
]
]

---
## Report structure revised in 2021 to address Council requests and improve synthesis

.pull-left[
* 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
]

.pull-right[
* 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
]

---
background-image: url("https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/SOE-MA-draft-03.16.23_Page_2.png")
background-size: 500px
background-position: right

## State of the Ecosystem Summary 2023: 
**Performance relative to management objectives - Mid-Atlantic**

.pull-left-60[
Seafood production ![:img decreasing arrow icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//decrease.png), ![:img below average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//below long term ave.png)

Profits ![:img decreasing arrow icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//decrease.png), ![:img below average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//below long term ave.png)

Recreational opportunities:  Effort ![:img increasing arrow icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//no trend.png) ![:img above average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//near-long-term-average.png); Effort diversity ![:img decreasing arrow icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//decrease.png) ![:img below average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//below long term ave.png)

Stability: Fishery ![:img no trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//no trend.png) ![:img near average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//near-long-term-average.png); Ecological ![:img mixed trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//Mixed trends.png) ![:img near average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//near-long-term-average.png)

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 ![:img mixed trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//Mixed trends.png) ![:img meeting objectives icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//checked.png)  
*  Recover endangered populations (NARW) ![:img decreasing arrow icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//decrease.png) ![:img below average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//below long term ave.png)  
]
.pull-right-40[]

---
background-image: url("https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//SOE-NE-final-03.27.23-508_Page_2.png")
background-size: 500px
background-position: right

## State of the Ecosystem Summary 2023: 
**Performance relative to management objectives - Georges Bank**

.pull-left-60[
Seafood production ![:img no trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//no trend.png), ![:img below average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//below long term ave.png)

Profits ![:img no trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//no trend.png), ![:img above average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//above long term ave.png)

Recreational opportunities:  Effort ![:img no trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//no trend.png), ![:img near average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//near-long-term-average.png); Effort diversity ![:img no trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//no trend.png), ![:img near average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//near-long-term-average.png)

Stability: Fishery ![:img mixed trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//Mixed trends.png), Commercial ![:img below average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//below long term ave.png) Rec ![:img near average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//near-long-term-average.png); Ecological ![:img mixed trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//Mixed trends.png) ![:img near average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//near-long-term-average.png)

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 ![:img mixed trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//Mixed trends.png) ![:img meeting objectives icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//checked.png)  
*  Recover endangered populations ![:img mixed trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//Mixed trends.png), NARW ![:img below average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//below long term ave.png) Gray seal ![:img above average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//above long term ave.png)  
]
.pull-right-40[]

---
background-image: url("https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//SOE-NE-final-03.27.23-508_Page_3.png")
background-size: 500px
background-position: right

## State of the Ecosystem Summary 2023: 
**Performance relative to management objectives - Gulf of Maine**

Profits Total ![:img no trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//no trend.png), ![:img above average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//above long term ave.png); NEFMC Managed ![:img decreasing arrow icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//decrease.png), ![:img below average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//below long term ave.png)

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 ![:img mixed trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//Mixed trends.png) ![:img meeting objectives icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//checked.png)  
*  Recover endangered populations ![:img mixed trend icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//Mixed trends.png), NARW ![:img below average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//below long term ave.png) Gray seal ![:img above average icon icon, 4%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//above long term ave.png) 
]
.pull-right-40[]

---
background-image: url("https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/SOE-MA-draft-03.16.23_Page_3.png")
background-size: 500px
background-position: right

## State of the Ecosystem Summary 2023: 
**Risks to meeting fishery management objectives - All regions**

.pull-left-60[
Climate: warming and changing oceanography continue
*  2022 among warmest years on record
*  Heat waves and Gulf Stream instability
*  Mid-Atlantic cold pool becoming warmer, smaller, and shorter in duration
*  Estuarine, coastal, and offshore habitats affected, with range of species responses
*  Distribution shifts complicate management
*  Gulf of Maine fall bloom highest in time series
*  Fish stocks with a mix of good and poor condition 
*  Multiple Mid-Atlantic stocks with declining productivity 
]

.pull-right-40[]

---
background-image: url("https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//SOE-NE-final-03.27.23-508_Page_4.png")
background-size: 500px
background-position: right

## State of the Ecosystem Summary 2023: 
**Risks to meeting fishery management objectives - All regions**

.pull-left-60[
Other ocean uses: offshore wind development
*  Rapid buildout in patchwork of areas 
*  Current revenue in proposed areas
    - 1-31% by port (some with EJ concerns)
    - Up to 17% annual commercial revenue
*  Different development impacts for species preferring soft bottom vs. hard bottom 
*  Overlap with known important right whale foraging habitats, increased vessel strike and noise risks 
*  Scientific survey mitigation in progress
*  Integrated Ecosystem Assessment is beginning for offshore wind and fisheries in the Gulf of Maine

]
.pull-right-40[]

---
# 2023 Performance relative to management objectives

.center[
![:img Fishing icon made by EDAB, 15%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//5_FISHING.png) &nbsp; &nbsp; &nbsp; ![:img Fishing industry icon made by EDAB, 15%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//6_INDUSTRY.png) &nbsp; &nbsp; &nbsp; ![:img Multiple drivers icon made by EDAB, 25%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//18.MULTIPLE_SYSTEM_DRIVERS.png) &nbsp; &nbsp; &nbsp; ![:img Spiritual cultural icon made by EDAB, 15%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//22.SPIRITUAL_CULTURAL.png) &nbsp; &nbsp; &nbsp; ![:img Protected species icon made by EDAB, 15%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//16.PROTECTEDSPECIES.png)
]

---
## Objective: Mid Atlantic Seafood production ![:img decreasing arrow icon, 2%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//decrease.png) ![:img below average icon icon, 2%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/below long term ave.png) &emsp; Risk elements: ComFood and RecFood, unchanged

.pull-left[
Indicators: Commercial landings, total and seafood

.contrib[
Key: Black = Landings of all species; Blue = Seafood landings; Red = MAFMC managed seafood landings
]

*Total landings now include Atlantic menhaden*

]

.pull-right[
Indicators: Recreational harvest
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-4-1.png" width="504" style="display: block; margin: auto;" />

]

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.
---
## Mid Atlantic Landings drivers: Stock status? TAC? &emsp; Risk elements: Fstatus, Bstatus, MgtControl

.pull-left[
Indicator: Stock status

.contrib[
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.  
]
]

.pull-right[

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

.contrib[
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.

---
.pull-left[
## Implications: Mid Atlantic Seafood Production

.table[
Biomass does not appear to drive landings trends
]

.contrib[
Key: Black = NEFSC survey; Red = NEAMAP survey
]
]

.pull-right[
.table[
* Declining seafood mainly benthos: surfclam/ocean quahog market drivers
]

<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-10-1.png" width="324" style="display: block; margin: auto;" />
.table[
* Declining total mainly planktivores: menhaden fishery consolidation
* 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
]
]

???
Stock status is above the minimum threshold for all but one stock, and aggregate biomass trends appear stable, so the decline in commercial seafood landings is most likely driven by market dynamics affecting the landings of surfclams and ocean quahogs, as landings have been below quotas for these species. The long term decline in total planktivore landings is largely driven by Atlantic menhaden fishery dynamics, including a consolidation of processors leading to reduced fishing capacity between the 1990s and mid-2000s.

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 
## GB ![:img no trend icon, 2%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//no trend.png) ![:img below average icon icon, 2%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/below long term ave.png) GOM ![:img decreasing arrow icon, 2%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/decrease.png) ![:img below average icon icon, 2%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/below long term ave.png)

Indicators: Commercial landings

<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-12-1.png" width="864" style="display: block; margin: auto;" />
.contrib[
Key: Black = Landings of all species; Blue = Seafood landings; Red = NEFMC managed seafood landings
]

---

.pull-left[
Indicators: Recreational harvest

<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-13-1.png" width="504" style="display: block; margin: auto;" />
]

.pull-right[

]

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.

---
## New England Landings drivers: Stock status

Indicator: Stock status

<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-15-1.png" width="720" style="display: block; margin: auto;" />
.contrib[
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
]

---
## New England Landings drivers

.pull-left[
Indicator: Survey biomass

]

.pull-right[

<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-17-1.png" width="576" style="display: block; margin: auto;" />
]

Biomass availability still seems unlikely driver

---

## Implications: New England Seafood Production
.pull-left[
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

]

.pull-right[

]
---

## Objective: New England Commercial Profits ![:img mixed trends arrow icon, 2%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/Mixed trends.png)
## GB ![:img above average icon icon, 2%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//above long term ave.png) GOM Total ![:img above average icon icon, 2%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//above long term ave.png), NEFMC-managed ![:img below average icon icon, 2%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/below long term ave.png)

Indicator: Commercial Revenue
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-20-1.png" width="792" style="display: block; margin: auto;" />

.contrib[
Key: Black = Revenue of all species combined; Red = Revenue of NEFMC managed species
]

---

.pull-left[
Indicator: Bennet--price and volume indices

]

.pull-right[
Implications:

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

]

---

## Objective: New England Environmental Justice and Social Vulnerability

Indicators: Environmental justice vulnerability, commercial fishery engagement and reliance

.pull-left[
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-22-1.png" width="468" style="display: block; margin: auto;" />
New England commercial fishing communities
]

.pull-right[

]

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.

---

## Objective: Mid Atlantic Environmental Justice and Social Vulnerability &emsp; Risk element: Social
Indicators: Environmental justice vulnerability, commercial fishery engagement and reliance 
.pull-left[
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-24-1.png" width="468" style="display: block; margin: auto;" />
Mid-Atlantic commercial fishing communities
]

.pull-right[

]

---
## Objective: Mid Atlantic Environmental Justice and Social Vulnerability &emsp; Risk element: Social 
Indicators: Environmental justice vulnerability, recreational fishery engagement and reliance 
.pull-left[
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-26-1.png" width="468" style="display: block; margin: auto;" />
Mid-Atlantic recreational fishing communities
]

.pull-right[
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-27-1.png" width="100%" style="display: block; margin: auto;" />

]

Implications: There was an increase in recreational fishing activities in the many of the top recreational communities from 2019 to 2020.

???
.contrib[
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.
]

---
# 2023 Risks to meeting fishery management objectives

.center[
![:img Climate icon made by EDAB, 25%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//3_CLIMATE.png) &nbsp; &nbsp; &nbsp; ![:img Wind icon made by EDAB, 25%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//24.WIND.png)
]

.center[
![:img Hydrography icon made by EDAB, 15%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//1_HYDROGRAPHY.png) &nbsp; &nbsp; &nbsp; ![:img Phytoplankon icon made by EDAB, 15%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//9_PHYTOPLANKTON.png) &nbsp; &nbsp; &nbsp; ![:img Forage fish icon made by EDAB, 15%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//13_FORAGEFISH.png) &nbsp; &nbsp; &nbsp; ![:img Apex predators icon made by EDAB, 15%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//17.APEXPREDATORS.png)  &nbsp; &nbsp; &nbsp; ![:img Other human uses icon made by EDAB, 15%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images//8_OTHERHUMANUSES.png) 
]

---

.pull-left[ 
## Risks: Climate change Mid Atlantic (a.k.a. indicator shock-and-awe)

Indicators: ocean currents, temperature, seasons
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-29-1.png" width="288" style="display: block; margin: auto;" />

<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-30-1.png" width="288" style="display: block; margin: auto;" />
]

.pull-right[

]

.table[
The Gulf Stream is trending north. Ocean summer is lasting longer. In contrast to SST, long term bottom temperature is increasing in all seasons. Few surface and no bottom extreme warming events in 2022.
]
.contrib[]
???
Seasonal sea surface temperatures in 2022 were above average for most of the year,  however late spring storms caused deep mixing, which delayed stratification and surface warming in late spring and early summer. A combination of long-term ocean warming and extreme events should be used to assess total heat stress on marine organisms

---
## Climate risks: offshore habitat

![:col_header Region, Indicator, Long term trend, Current status]
![:col_row 
 Coastwide 
 
 
 Mid-Atlantic 
 
 
 
 
 
 
 
 Georges Bank 
 
 
 
 
 Gulf of Maine 
 
 
 
 ,
 
 Gulf stream index 
 Warm core rings 
 
 Sea surface temperature 
 Sea bottom temperature 
 Summer length 
 Extreme temperature events 
 Cold pool temperature 
 Cold pool duration 
 Cold pool extent 
 
 Sea surface temperature 
 Sea bottom temperature 
 Summer length 
 Extreme temperature events 
 
 Sea surface temperature 
 Sea bottom temperature 
 Summer length 
 Extreme temperature events 
 Warm slope water NE channel 
 , 
 
 Moving north 
 More numerous 
 
 Increasing 
 Increasing 
 Increasing 
 No trend 
 Increasing 
 Decreasing 
 Decreasing 
 
 Increasing 
 Increasing 
 Increasing 
 No trend 
 
 Increasing 
 Increasing 
 Increasing 
 No trend 
 Increasing 
 ,
 
 &plus; 
 high regime 
 
 &plus; 
 &plus; 
 &plus; 
 2 of 9-11 days 
 &plus; 
 &minus; 
 &minus; 
 
 &plus; 
 &plus; 
 &plus; 
 1 of 28 days 
 
 &plus; 
 &plus; 
 &plus; 
 4 of 5 to 8 days 
 &plus; 
 
 
]

???
Needs: skillful short term projections (2-5 years) of multiple habitat variables at regional scale

---
## Implications: Climate change and managed species &emsp; Risk based on climate vulnerability:

.pull-left[
Climate: 18 low, 10 low-mod, 9 mod-high, 3 high risk

*Multiple drivers with different impacts by species*    
* Seasonal estuarine conditions affect life stages of managed species differently
* Ocean acidification impact on commercial species  
![:img Mid Seasonal pH](https://github.com/NOAA-EDAB/ecodata/raw/master/workshop/images/Saba_Fig_SOE_MAFMC.jpg)

* Warm core rings important to *Illex* availability. 
]

.pull-right[
DistShift: 2 low, 4 low-mod, 31 mod-high, 3 high risk

*New Indicator: protected species shifts*
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-31-1.png" width="504" style="display: block; margin: auto;" />
]

???
.contrib[
+ Chesapeake suitable habitat for juvenile summer flounder growth has declined by 50% or more 
+ Climate change is expected to continue impacting habitat function and use for multiple species 
+ Habitat improving in some areas (tidal fresh SAV, oyster reefs), but eelgrass declining 
] 
.contrib[
+ Scallops and longfin squid in Long Island Sound and off New Jersey have experienced low aragonite
+ Areas of low pH identified in surfclam and scallop habitat 
+ Lab work identified pH thresholds for surfclam growth
] 
.contrib[
+ Fishing effort concentrates on the eastern edge of warm core rings, where upwelling and enhanced productivity ocurr. 
+ Fuel cost, plentiful longfin, and fewer warm core rings near the shelf led to lower *Illex* catch in 2022.
]
.contrib[
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. 
]
---
.pull-left-60[
## Risks: Ecosystem productivity Mid Atlantic; Element: EcoProd

Indicator: Fish condition 
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-32-1.png" width="120%" style="display: block; margin: auto;" />

Indicator: Fish productivity anomaly &rarr;

Implications: 
Species in the MAB had mixed condition in 2022. Fish productivity based on surveys and assessments has been below average.

]

.pull-right-40[
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-33-1.png" width="504" style="display: block; margin: auto;" />

<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-34-1.png" width="504" style="display: block; margin: auto;" />
.contrib[
Black line indicates sum where there are the same number of assessments across years.
]
]

???
Methods from <a name=cite-perretti_regime_2017></a>([Perretti, et al., 2017](http://www.int-res.com/abstracts/meps/v574/p1-11/)).

---
.pull-left[
## Risks: Ecosystem structure New England

Indicator: Forage fish index
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-35-1.png" width="504" style="display: block; margin: auto;" />

]

.pull-right[
Indicator: Common tern productivity
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-36-1.png" width="504" style="display: block; margin: auto;" />

Indicator: Gray seal pup production
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-37-1.png" width="504" style="display: block; margin: auto;" />
]

---
## Risks: Offshore Wind Development Mid Atlantic &emsp; Element: OceanUse

.pull-left[
Indicators: development timeline, fishery and community specific revenue in lease areas

Council request: which New England ports have significant reliance on Mid-Atlantic managed species?

]

.pull-right[
<img src="20230523_SOE_Seminar_Gaichas_files/figure-html/unnamed-chunk-39-1.png" width="504" style="display: block; margin: auto;" />
]

---

background-image: url("https://github.com/NOAA-EDAB/ecodata/raw/master/workshop/images/SOE_2023_right_whales_hatteras_frame_v3.jpg")
background-size: 500px
background-position: right

## Risks: Offshore Wind Development Summary

.pull-left[
Implications: 
*  1-34% 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 17% 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 important 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.
]
.pull-right[]

???
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.

---
## EAFM Risk Assessment: 2023 Update (all methods to be reviewed/revised this year)

.pull-left[
*Species level risk elements*
<table class="risktable table" style="font-size: 9px; margin-left: auto; margin-right: auto;">
 <thead>
 <tr>
 <th style="text-align:left;"> Species </th>
 <th style="text-align:left;"> Assess </th>
 <th style="text-align:left;"> Fstatus </th>
 <th style="text-align:left;"> Bstatus </th>
 <th style="text-align:left;"> FW1Pred </th>
 <th style="text-align:left;"> FW1Prey </th>
 <th style="text-align:left;"> FW2Prey </th>
 <th style="text-align:left;"> Climate </th>
 <th style="text-align:left;"> DistShift </th>
 <th style="text-align:left;"> EstHabitat </th>
 </tr>
 </thead>
<tbody>
 <tr>
 <td style="text-align:left;"> Ocean Quahog </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Surfclam </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Summer flounder </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Scup </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Black sea bass </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Atl. mackerel </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Chub mackerel </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Butterfish </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Longfin squid </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Shortfin squid </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Golden tilefish </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Blueline tilefish </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Bluefish </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Spiny dogfish </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Monkfish </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Unmanaged forage </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Deepsea corals </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 </tr>
</tbody>
</table>
.contrib[
* RT assessment decreased Spiny dogfish **Assess**, risk to low and increased **Fstatus** risk to high
* RT assessment decreased bluefish **Bstatus** risk from high to low-moderate
* RT assessment increased Illex **Assess** risk from low-moderate to high
]

*Ecosystem level risk elements*
<table class="risktable table" style="font-size: 9px; margin-left: auto; margin-right: auto;">
 <thead>
 <tr>
 <th style="text-align:left;"> System </th>
 <th style="text-align:left;"> EcoProd </th>
 <th style="text-align:left;"> CommRev </th>
 <th style="text-align:left;"> RecVal </th>
 <th style="text-align:left;"> FishRes1 </th>
 <th style="text-align:left;"> FishRes4 </th>
 <th style="text-align:left;"> FleetDiv </th>
 <th style="text-align:left;"> Social </th>
 <th style="text-align:left;"> ComFood </th>
 <th style="text-align:left;"> RecFood </th>
 </tr>
 </thead>
<tbody>
 <tr>
 <td style="text-align:left;"> Mid-Atlantic </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> modhigh </td>
 </tr>
</tbody>
</table>
.contrib[
* Recreational value risk decreased from low-moderate to low
] 
]

.pull-right[ 
*Species and Sector level risk elements*
<table class="risktable table" style="font-size: 11px; margin-left: auto; margin-right: auto;">
 <thead>
 <tr>
 <th style="text-align:left;"> Species </th>
 <th style="text-align:left;"> MgtControl </th>
 <th style="text-align:left;"> TecInteract </th>
 <th style="text-align:left;"> OceanUse </th>
 <th style="text-align:left;"> RegComplex </th>
 <th style="text-align:left;"> Discards </th>
 <th style="text-align:left;"> Allocation </th>
 </tr>
 </thead>
<tbody>
 <tr>
 <td style="text-align:left;"> Ocean Quahog-C </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Surfclam-C </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Summer flounder-R </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> highest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Summer flounder-C </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Scup-R </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Scup-C </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Black sea bass-R </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> highest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Black sea bass-C </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Atl. mackerel-R </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Atl. mackerel-C </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> highest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Butterfish-C </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Longfin squid-C </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Shortfin squid-C </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> highest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Golden tilefish-R </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Golden tilefish-C </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Blueline tilefish-R </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Blueline tilefish-C </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Bluefish-R </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> highest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Bluefish-C </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Spiny dogfish-R </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Spiny dogfish-C </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Chub mackerel-C </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowmod </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Unmanaged forage </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 <td style="text-align:left;"> lowest </td>
 </tr>
 <tr>
 <td style="text-align:left;"> Deepsea corals </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> modhigh </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 <td style="text-align:left;"> na </td>
 </tr>
</tbody>
</table>
.contrib[
* Management section not updated--to be revised this year 
]
]

???
Comments on overall risk assessment for EOP to consider?

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## Priority requests from managers

.pull-left-60[

*  Highest priority requests in progress
    -  System level thresholds and reference points
    -  Trend analysis, inflections and break points
    -  Regime shifts
*  Identified some gaps
    - Short term forecasts
    - Management complexity
    - Recreational bycatch
*  Stock level indicators best addressed in assessment?

![:img bluefish ESP conceptual model, 90%](https://github.com/NOAA-EDAB/presentations/raw/master/docs/EDAB_images/bluefishconceptualmodel.png)
]

.pull-right-40[
]

???

The Bluefish Research Track ESP was presented December 7 2022, and was well received by CIE reviewers. Reviewers commented that it was the most complete treatment of a stock assessment "ecosystem ToR" they had seen, and formed a good basis for integrating further ecosystem information into the stock assessment in the future. The full ESP document is available as a working paper from the [stock assessment data portal](https://apps-nefsc.fisheries.noaa.gov/saw/sasi_files.php?year=2022&species_id=32&stock_id=6&review_type_id=5&info_type_id=5&map_type_id=&filename=WP%2001%20Tyrell%20etAl%202022%20-%20ESP.pdf).

In addition to the conceptual model, a summary table was developed for bluefish ecosystem indicators. This type of summary could contribute to OFL CV decisions with further information on how these indicator levels affect uncertainty in assessment.

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## THANK YOU! SOEs made possible by (at least) 71 contributors from 20+ institutions

.table[
![:col_row 
 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 (U Connecticut) 
 Joseph Caracappa 
 Doug Christel (GARFO) 
 Patricia Clay 
 Lisa Colburn 
 Jennifer Cudney (NMFS Atlantic HMS Management Division) 
 Tobey Curtis (NMFS Atlantic HMS Management Division) 
 Art Degaetano (Cornell U) 
 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 (Virginia Institute of Marine Science) 
 Sarah Gaichas 
 Ben Galuardi (GARFO) 
 Avijit Gangopadhyay (School for Marine Science and Technology UMass Dartmouth) 
 James Gartland (Virginia Institute of Marine Science),
 
 Lori Garzio (Rutgers University) 
 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 
 Gabe Larouche (Cornell U) 
 Daniel Linden 
 Andrew Lipsky 
 Sean Lucey 
 Don Lyons (National Audubon Society’s Seabird Restoration Program) 
 Chris Melrose 
 Shannon Meseck 
 Ryan Morse 
 Ray Mroch (SEFSC) 
 Brandon Muffley (MAFMC) 
 Kimberly Murray 
 Janet Nye (University of North Carolina at Chapel Hill) 
 Chris Orphanides 
 Richard Pace 
 Debi Palka 
 Tom Parham (Maryland DNR),
 
 Charles Perretti 
 CJ Pellerin (NOAA Chesapeake Bay Office) 
 Kristin Precoda 
 Grace Roskar (NMFS Office of Habitat Conservation) 
 Grace Saba (Rutgers) 
 Vincent Saba 
 Sarah Salois 
 Chris Schillaci (GARFO) 
 Amy Schueller (SEFSC) 
 Teresa Schwemmer (Stony Brook University) 
 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 
 Timothy White (Environmental Studies Program BOEM) 
 Sarah Wilkin (NMFS Office of Protected Resources) 
 Mark Wuenschel ]
]

???

---
## Additional resources
.pull-left[
* [SOE Reports on the web](https://www.fisheries.noaa.gov/new-england-mid-atlantic/ecosystems/state-ecosystem-reports-northeast-us-shelf)
* [ecodata R package](https://github.com/noaa-edab/ecodata)
* [SOE Technical Documentation](https://noaa-edab.github.io/tech-doc)
* [Draft indicator catalog](https://noaa-edab.github.io/catalog/)

.contrib[

* Slides available at https://noaa-edab.github.io/presentations
* Contact: <Sarah.Gaichas@noaa.gov>
]
]

.pull-right[
* Visualizations:
  * [Mid-Atlantic Human Dimensions indicators](http://noaa-edab.github.io/ecodata/human_dimensions_MAB)
  * [Mid-Atlantic Macrofauna indicators](http://noaa-edab.github.io/ecodata/macrofauna_MAB)
  * [Mid-Atlantic Lower trophic level indicators](https://noaa-edab.github.io/ecodata/LTL_MAB)
  * [New England Human Dimensions indicators](http://noaa-edab.github.io/ecodata/human_dimensions_NE)
  * [New England Macrofauna indicators](http://noaa-edab.github.io/ecodata/macrofauna_NE)
  * [New England Lower trophic level indicators](https://noaa-edab.github.io/ecodata/LTL_NE)
]

## References

.contrib[
<a name=bib-bastille_improving_2021></a>[Bastille, K. et
al.](#cite-bastille_improving_2021) (2021). "Improving the IEA Approach
Using Principles of Open Data Science". In: _Coastal Management_ 49.1.
Publisher: Taylor & Francis \_ eprint:
https://doi.org/10.1080/08920753.2021.1846155, pp. 72-89. ISSN:
0892-0753. DOI:
[10.1080/08920753.2021.1846155](https://doi.org/10.1080%2F08920753.2021.1846155).
URL:
[https://doi.org/10.1080/08920753.2021.1846155](https://doi.org/10.1080/08920753.2021.1846155)
(visited on Apr. 16, 2021).

<a name=bib-depiper_operationalizing_2017></a>[DePiper, G. S. et
al.](#cite-depiper_operationalizing_2017) (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](https://doi.org/10.1093%2Ficesjms%2Ffsx038).
URL:
[https://academic.oup.com/icesjms/article/74/8/2076/3094701](https://academic.oup.com/icesjms/article/74/8/2076/3094701)
(visited on Mar. 09, 2018).

<a name=bib-depiper_learning_2021></a>[DePiper, G. et
al.](#cite-depiper_learning_2021) (2021). "Learning by doing:
collaborative conceptual modelling as a path forward in ecosystem-based
management". In: _ICES Journal of Marine Science_. ISSN: 1054-3139.
DOI:
[10.1093/icesjms/fsab054](https://doi.org/10.1093%2Ficesjms%2Ffsab054).
URL:
[https://doi.org/10.1093/icesjms/fsab054](https://doi.org/10.1093/icesjms/fsab054)
(visited on Apr. 15, 2021).

<a name=bib-gaichas_implementing_2018></a>[Gaichas, S. K. et
al.](#cite-gaichas_implementing_2018) (2018). "Implementing Ecosystem
Approaches to Fishery Management: Risk Assessment in the US
Mid-Atlantic". In: _Frontiers in Marine Science_ 5. ISSN: 2296-7745.
DOI:
[10.3389/fmars.2018.00442](https://doi.org/10.3389%2Ffmars.2018.00442).
URL:
[https://www.frontiersin.org/articles/10.3389/fmars.2018.00442/abstract](https://www.frontiersin.org/articles/10.3389/fmars.2018.00442/abstract)
(visited on Nov. 20, 2018).

<a name=bib-muffley_there_2021></a>[Muffley, B. et
al.](#cite-muffley_there_2021) (2021). "There Is no I in EAFM Adapting
Integrated Ecosystem Assessment for Mid-Atlantic Fisheries Management".
In: _Coastal Management_ 49.1. Publisher: Taylor & Francis \_ eprint:
https://doi.org/10.1080/08920753.2021.1846156, pp. 90-106. ISSN:
0892-0753. DOI:
[10.1080/08920753.2021.1846156](https://doi.org/10.1080%2F08920753.2021.1846156).
URL:
[https://doi.org/10.1080/08920753.2021.1846156](https://doi.org/10.1080/08920753.2021.1846156)
(visited on Apr. 16, 2021).

<a name=bib-perretti_regime_2017></a>[Perretti, C. et
al.](#cite-perretti_regime_2017) (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](https://doi.org/10.3354%2Fmeps12183). URL:
[http://www.int-res.com/abstracts/meps/v574/p1-11/](http://www.int-res.com/abstracts/meps/v574/p1-11/)
(visited on Feb. 10, 2022).
]

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.right[
 
 
 
 
 
 
 
 
 
 
# Thank you!

# Questions?
]