Summer flounder (Paralichthys dentatus) are found in inshore and offshore waters from Nova Scotia, Canada to the east coast of Florida. In the U.S., they are most abundant in the Mid-Atlantic region from Cape Cod, Massachusetts to Cape Fear, North Carolina.
Summer flounder usually begin to spawn at age two or three, at lengths of about 10 inches. Spawning occurs in the fall while the fish are moving offshore. Spawning migration is linked to sexual maturity, with the oldest and largest fish migrating first. As in their seasonal migrations, spawning summer flounder in the northern portion of the geographic range spawn and move offshore (depths of 120 to 600 feet) earlier than those in the southern part of the range. Larvae migrate to inshore coastal and estuarine areas from October to May. The larvae, or fry, move to bottom waters upon reaching the coast and spend their first year in bays and other inshore areas. At the end of their first year, some juveniles join the adult offshore migration.
Adults spend most of their life on or near the sea bottom burrowing in the sandy substrate. Flounder lie in ambush and wait for their prey. They are quick and efficient predators with well-developed teeth allowing them to capture small fish, squid, sea worms, shrimp, and other crustaceans.
Summer flounder are one of the most sought after commercial and recreational fish along the Atlantic coast, with total landings at approximately 13.7 million pounds in 2018. Using baseline data from 1980 to 1989, the current plan allocates the summer flounder quota on a 60/40 percent basis to commercial and recreational fisheries, respectively.
Two major commercial trawl fisheries exist — a winter offshore and a summer inshore. Summer flounder are also taken by pound nets and gillnets in estuarine waters. Throughout the 1980s, commercial landings ranged from 21 to 38 million pounds. By 1990, landings reached a low of nine million pounds and have since fluctuated between nine and 17 million pounds. In 1993, the coastwide quota was implemented for the first time, setting a commercial landings limit of 12.35 million pounds. Commercial quotas have since ranged from 5.66 to 18.18 million pounds. Commercial landings (which are limited by the quota) have ranged from 8.81 million pounds to 18.17 million pounds since 1993. Over the past five years, commercial landings have been on the decline, in part due to annual quota limits, dropping from 10.6 million pounds in 2015 to 6.1 million pounds in 2018.
Summer flounder are also highly prized in the recreational fishery. Anglers catch summer flounder from the shore, piers, and boats with hook and line. From 1980 through 2004, recreational landings varied widely from a high of 38 million pounds in 1980 to a low of three million pounds in 1989. Starting in 1993, harvest limits were implemented for the recreational fishery. Recreational harvest from 2005 to present has also shown a steady decline, in part due to declines in the coastwide recreational harvest limit (RHL). In 2018, recreational anglers harvested 7.6 million pounds of summer flounder.
Although reported landings have equaled or only slightly exceeded commercial quotas and recreational harvest limits in recent years, there is evidence of substantial illegal harvest in the form of unreported, underreported, or misreported landings. In 2013 and 2014, two separate investigations revealed that large quantities of summer flounder were being taken illegally under the guise of quota acquired through the Council’s Research Set-Aside (RSA) program (the Council subsequently suspended the program in order to consider alternative cooperative research options). There may also be substantial non-RSA related illegal/unreported landings, although fewer details are available on the extent of unreported landings outside of the RSA program. While the exact amount of illegally harvested summer flounder is not known, the effect may have resulted in substantial overages of the fishery’s annual catch limits (ACLs).
The 2018 benchmark stock assessment and peer review indicate that summer flounder is not overfished nor experiencing overfishing. Spawning stock biomass (SSB) is estimated at 98 million pounds, approximately 78% of the SSB target of 126 million pounds. Fishing mortality is estimated to be 0.334, below the fishing mortality threshold of 0.448. Recruitment was estimated at 42 million fish at age 0, below the time series average of 53 million fish at age 0. Recruitment has been below average since 2011.
Data analyzed by the Northeast Fisheries Science Center for the assessment indicate increasing relative abundance of older fish and an expanding age structure. However, the data also indicate a decrease in relative total abundance since the late 2000s, as well as decreasing trends in average lengths and weights at age for both sexes, suggesting slower growth and delayed maturity which impacts the biological reference points. The assessment shows current mortality from all sources is greater than recent recruitment inputs to the stock, which has resulted in a declining stock trend. Additionally, the assessment found the spatial distribution of the resource is continuing to shift northward and eastward.
A key attribute of the assessment is the incorporation of revised recreational catch data. In July 2018, MRIP revised the previous recreational catch estimates with a calibrated 1982-2017 time series that corresponds to the new MRIP survey methods. For comparison with the previous estimates, the revised estimates of 2017 recreational landings and discards are over three times the previous estimates. The revised recreational catch estimates increased the 1982-2017 total annual catch by an average of 29%, ranging from 11% increase in 1989 to 43 percent increase in 2017. The increase in estimated removals resulted in an increased population estimate compared to previous assessments.
Recreational angler with summer flounder. Photo credit: Mark Terceiro, NMFS NEFSC.
The Commission approved the first Fishery Management Plan (FMP) for Summer Flounder in 1982, followed by a similar FMP approved by the MAFMC in 1988. Since then, both agencies have made significant revisions to the plan, increasing the protection of juvenile fish and ensuring the maintenance of an adequate spawning population. This increased protection has been implemented through larger minimum size limits across all sectors, increased mesh sizes, and decreased recreational possession limits. Cumulatively, these changes have contributed to conserving the resource while maintaining important commercial and recreational fisheries. This is not to say that challenges in managing this species do not still exist. Issues related to sector allocation and annual harvest levels persist.
In December 2018, the Board approved Addenda XXXI and XXXII to the FMP. Addendum XXXI adds to the suite of tools available for management, with particular focus on enhancing the compatibility of state and federal regulations, by allowing the use of conservation equivalency for recreational management starting in 2020. Conservation equivalency allows recreational management measures in federal waters measures to be waived, and instead requires recreational anglers to abide by the measures of the state in which they land their catch. The Board and Council will annually decide whether to enact conservation equivalency.
Addendum XXXII establishes an annual specifications process for developing recreational management measures. The Board will approve regional measures in early spring each year, based on technical committee analysis of stock status, resource availability, and harvest estimates. Public input on specifications will be gathered by states through their individual public comment processes. The specifications process will provide the Board more flexibility in adjusting measures, if necessary, to constrain harvest to the annual coastwide RHL. Further, the process will enable the Board to consider a host of factors, including: regional equity; regulatory stability; species abundance and distribution; and late-breaking recreational harvest estimates.
Based on the 2018 stock assessment findings, the Board and MAFMC revised the 2019 specifications and set new specifications for 2020 and 2021, with the intent to maintain regulatory stability. For the 2019-2021 fishing seasons, the commercial quota is set at 11.53 million pounds and the recreational harvest limit (RHL) is set at 7.69 million pounds. The revised commercial quota was approximately a 49% increase over the previously set 2019 quota. While the revised 2019 RHL represents an approximate 49% increase over the previously set 2019 RHL, the Board chose to maintain status quo recreational measures, which are projected to achieve a harvest level close to the revised RHL based on the calibrated MRIP recreational harvest data.
In January 2021, the Board and MAFMC approved for public comment the Summer Flounder, Scup and Black Sea Bass Commercial/Recreational Allocation Amendment. Comments may be submitted at any of the 5 virtual public hearings to be held between February 17 and March 2, 2021 or via written comment until March 16, 2021. The Board and MAFMC are developing this joint amendment to consider adjusting the allocations of catch or landings between the commercial and recreational fisheries for summer flounder, scup and black sea bass. The commercial and recreational allocations for all three species are currently based on historical proportions of landings (for summer flounder and black sea bass) of catch (for scup) for each sector. Recent changes in how recreational catch is estimated have resulted in a discrepancy between the current levels of estimated recreational harvest and the allocations of summer flounder, scup and black sea bass to the recreational sector. Some changes have also been made to commercial catch data since the allocations were established. This amendment considers whether modifications to the allocations are needed in light of these and other changes in the fisheries. The amendment also considers options that would allow a portion of landings to be transferred between the commercial and recreational sectors each year, in either direction, based on the needs of each sector. Public comment is being accepted until March 16, 2021 (see a link to the public hearing document under Pending Actions below). A video of the public hearing Powerpoint presentation can be accessed here.