Layer type(s): Wild-Caught Fisheries sub-goal layer
Data description:
Stock assessment information was provided for 46 individual stocks via data request from the National Marine Fisheries Service for all stocks in the greater Northeast region from 2004 - 2018. Specifically, the metrics B/Bmsy and F/Fmsy (when available) were provided for the years in which they were assessed. Additional stock assessment information for species not in the NMFS stock assessment database were available in the RAM Legacy Stock Assessment database, this resulted in four additional stocks. Stock assessments for American lobster were collected from the Atlantic States Marine Fisheries Commission documents.
Assessment source | Stock | Metrics |
---|---|---|
ASMFC | American lobster, Gulf of Maine | B/Bmsy, F/Fmsy |
ASMFC | American lobster, Southern New England | B/Bmsy, F/Fmsy |
NMFS | Acadian redfish | B/Bmsy, F/Fmsy |
NMFS | American plaice | B/Bmsy, F/Fmsy |
NMFS | Atlantic cod, George’s Bank | B/Bmsy, F/Fmsy |
NMFS | Atlantic cod, Gulf of Maine | B/Bmsy, F/Fmsy |
NMFS | Atlanic halibut | B/Bmsy, F/Fmsy |
NMFS | Atlantic herring | B/Bmsy, F/Fmsy |
NMFS | Atlantic mackerel | B/Bmsy, F/Fmsy |
NMFS | Surf clam | B/Bmsy, F/Fmsy |
NMFS | Atlantic wolffish | B/Bmsy, F/Fmsy |
NMFS | Barndoor skate | B/Bmsy |
NMFS | Black sea bass | B/Bmsy, F/Fmsy |
NMFS | Bluefish | B/Bmsy, F/Fmsy |
NMFS | Butterfish | B/Bmsy, F/Fmsy |
NMFS | Clearnose skate | B/Bmsy |
NMFS | Monkfish/anglerfish/goosefish, Gulf of Maine/Northern Georges Bank | B/Bmsy, F/Fmsy |
NMFS | Monkfish/anglerfish/goosefish, Southern Georges Bank/Mid-Atlantic | B/Bmsy, F/Fmsy |
NMFS | Haddock, George’s Bank | B/Bmsy, F/Fmsy |
NMFS | Haddock, Gulf of Maine | B/Bmsy, F/Fmsy |
NMFS | Little (Summer) skate | B/Bmsy |
NMFS | Squid/Loligo | |
NMFS | Ocean pout | B/Bmsy, F/Fmsy |
NMFS | Ocean quahog | B/Bmsy, F/Fmsy |
NMFS | Pollock | B/Bmsy, F/Fmsy |
NMFS | Red hake, Gulf of Maine/Northern Georges Bank | B/Bmsy, F/Fmsy |
NMFS | Red hake, Southern Georges Bank/Mid-Atlantic | B/Bmsy, F/Fmsy |
NMFS | Scup/Porgy | B/Bmsy, F/Fmsy |
NMFS | Sea scallop | B/Bmsy, F/Fmsy |
NMFS | Silver hake/Whiting, Gulf of Maine/Northern Georges Bank | B/Bmsy, F/Fmsy |
NMFS | Silver hake/Whiting, Southern Georges Bank/Mid-Atlantic | B/Bmsy, F/Fmsy |
NMFS | Smooth skate | B/Bmsy |
NMFS | Spiny dogfish | B/Bmsy, F/Fmsy |
NMFS | Summer flounder | B/Bmsy, F/Fmsy |
NMFS | Thorny skate | B/Bmsy |
NMFS | Tilefish | B/Bmsy, F/Fmsy |
NMFS | Blueline tilefish | B/Bmsy, F/Fmsy |
NMFS | Golden tilefish | B/Bmsy, F/Fmsy |
NMFS | White hake | B/Bmsy, F/Fmsy |
NMFS | Sand-dab flounder/Windowpane/Brill, Gulf of Maine/Georges Bank | B/Bmsy, F/Fmsy |
NMFS | Sand-dab flounder/Windowpane/Brill, Southern New England/Mid-Atlantic | B/Bmsy, F/Fmsy |
NMFS | Winter flounder, Georges Bank | B/Bmsy, F/Fmsy |
NMFS | Winter flounder, Southern New England/Mid-Atlantic | B/Bmsy, F/Fmsy |
NMFS | Winter flounder, Gulf of Maine | B/Bmsy, F/Fmsy |
NMFS | Winter skate | B/Bmsy |
NMFS | Witch flounder | B/Bmsy, F/Fmsy |
NMFS | Yellowtail flounder, Cape Cod/Gulf of Maine | B/Bmsy, F/Fmsy |
NMFS | Yellowtail flounder, Georges Bank | B/Bmsy, F/Fmsy |
NMFS | Yellowtail flounder, Southern New England/Mid-Atlantic | B/Bmsy, F/Fmsy |
RAM | Menhaden | B/Bmsy, F/Fmsy |
RAM | Skipjack tuna | B/Bmsy, F/Fmsy |
RAM | Striped bass | B/Bmsy, F/Fmsy |
RAM | Weakfish | B/Bmsy |
Each stock is rescaled to be between 0 (least sustainable) and 1 (most sustainable) using stock assessment metrics \(B/B_{MSY}\) and, when available, \(F/F_{MSY}\).
The amount of biomass in the water (\(B\)) compared to the amount of biomass that can be harvested at maximum sustainable yield (\(B_{MSY}\)) provides a metric for knowing whether a single stock is fully exploited (0.8 < \(B/B_{MSY}\) < 1.2), overfished (\(B/B_{MSY}\) < 0.8) or underfished (\(B/B_{MSY}\) > 1.2). The stock biomass score (\(B'\)) for each stock is calculated based on \(B/B_{MSY}\), where
\[ B' = \begin{cases} B/B_{MSY},& B/B_{MSY} < 0.8,\\ 1,& 0.8 < B/B_{MSY} < 1.2, \\ \frac{thresh - B/B_{MSY}}{thresh-pen} , & 1.2 < B/B_{MSY} < 3.0,\\ 0.25, & B/B_{MSY} >= 3.0 \end{cases}\]
underexploitation penalty, \(pen\) = 0.25 (a stock can not receive lower than 0.25 if underexploited)
underxploitation threshold, \(thresh\) = 3 (once a stock has a \(B/B_{MSY}\) of 3 or greater, it will receive a score of 0.25)
Rescaled fishing mortality F’ for each stock is calculated for stocks that have an assessed fishing mortality rate (\(F/F_{MSY}\)). This allows scores to reflect whether management actions have been taken to reduce fishing pressure, in particular for stocks that are overfished. As such, if a stock is overfished (B/BMSY < 0.8) but F/FMSY is reduced to account for rebuilding, F’ is set to 1 and the stock can receive the highest score of 1. A three year rolling-mean is also applied to \(F'\) since fishing mortality fluctuate significantly in a short amount of time in response to a management decision. . This is not done for \(B`\) as it is a less sensitive metric since it relies on biological processes.
When \(B/B_{MSY}\) >= 0.8, a perfect score of 1 is assigned if \(F/F_{MSY}\) is between 0.66 and 1.2. If \(F/F_{MSY}\) is greater than 1.2, \(F`\) decreases linearly towards 0, and once \(F/F_{MSY}\) is greater than 2.0, indicating overfishing, \(F`\) goes to 0. If \(F/F_{MSY}\) is less than 0.66, indicating underfishing, \(F`\) decreases linearly to a minimum score of 0.25.
\[ F' = \begin{cases} 0,& F/F_{MSY} >= 2.0,\\ \frac{2 - F/F_{MSY}}{0.8},& 1.2 < F/F_{MSY} < 2.0, \\ 1 , & 0.66 < F/F_{MSY} < 1.2, \\ 0.25 + \frac{0.75F/F_{MSY}}{0.66},& F/F_{MSY} < 0.66 \end{cases}\]
When \(B/B_{MSY}\) < 0.8 & \(F/F_{MSY}\) < 2.0, the model is altered to allow for low levels of fishing (\(F/F_{MSY}\)) for overfished stocks as a management measure. In these cases, \(F/F_{MSY}\) is first translated into a new parameter, \(F\) based on the slope of the line from from \(B/B_{MSY} = 0.8\) to \(0\):
\[F = F/F_{MSY} + \frac{1.2 - B/B_{MSY}}{0.7}\] then,
\[ F' = \begin{cases} 0,& F >= 2.0,\\ \frac{2 - F}{0.8},& 1.2 < F < 2.0, \\ 1 , & 0.66 < F < 1.2, \\ 0.25 + \frac{0.75F}{0.66},& F < 0.66 \end{cases}\]
The final stock score (\(SS\)) is the product of \(B`\) and \(F`\). If only \(B/B_{MSY}\) is available, \(SS = B`\).
\[ SS = F'*B'\]
Here is an example of how \(B/B_{MSY}\) and \(F/F_{MSY}\) values are turned into stock scores between 0 and 1 for Pollock in the Gulf of Maine/Georges Bank:
Wild-Caught Fisheries goal layer
The final stock status layer lists each stock and it’s stock score between 0 and 1. This is then combined with the fisheries landings data in the Wild-Caught Fisheries model to match stocks with the regions in which they are caught, and their stock scores are catch-weighted according to the proportional catch each stock makes up for each region.
Gapfilling
Stock assessments are not performed every year for every managed stock in a region. This necessitates some gapfilling for years where information is not provided. All missing values for \(B/B_{MSY}\) and \(F/F_{MSY}\) were gapfilled with the most recent known value.
References
National Marine Fisheries Service. (2018). Stock assessment data for the Northeast and Mid-Atlantic stocks managed by NOAA. Provided via email from Jefferey Vieser. 14 December 2018.
RAM Legacy Stock Assessment Database. (2020). RAM Legacy Stock Assessment Database v4.491 (Version v4.491) [Data set]. Zenodo. http://doi.org/10.5281/zenodo.3676088