Based on the most recent data from the James, Potomac, Rappahannock, Susquehanna and York rivers, the estimate of Chesapeake Bay-wide American shad abundance increased in 2012 to 38 percent of the goal.
The Potomac River has seen the most consistent increase of returning shad, reaching 120 percent of that river’s target. The York River’s shad abundance is at 18 percent of the target, the lower James is at 17, the Rappahannock is at 92 while the upper James and Susquehanna rivers remain at less than 1 percent.
Date created: Oct 24 2013 / Download
American shad were once the most abundant and economically important species in the Chesapeake Bay. Shad are anadromous fish and spend most of their lives in the ocean, returning to freshwater rivers to spawn after they reach maturity. Data for the York, Potomac, Rappahannock and lower James Rivers were provided by the Virginia Institute of Marine Science via an ongoing Catch per Unit Effort (CPUE) study involving American Shad gill-netting. Data for the Susquehanna and upper James Rivers represent published fishway passage values for Conowingo and Boshers Dams, respectively.
What are American shad and why are they important to the Chesapeake Bay? Bruce Vogt from the National Oceanic and Atmospheric Administration (NOAA) explains how the watershed’s shad population has changed over time and what scientists are doing to restore the anadromous fish to our waterways.
Learn more about shad in the Chesapeake Bay Program’s online Field Guide.
Produced by Steve Droter
Stock Footage: Photography by Michelson, Inc. and Jim Thompson, MD DNR
Photos: Library of Congress, LC-DIG-ggbain-18896, LC-DIG-hec-06375
Music: “A Moment of Jazz” by Ancelin
Historically, local economies flourished from the annual shad run in the spring, when the fishes’ upriver migration begins. But shad populations were decimated in the 1970s by overfishing, pollution, and dams and other blockages that prevent the fish from reaching their upstream spawning grounds.
Spawning shad stocks are tracked in five major river systems, each with its own numeric target to meet or exceed:
Potomac River: 31.1 CPUE running average
Rappahannock River: 7.85 CPUE
Susquehanna River: Two million shad passing York Haven Dam annually
York River: 17.4 CPUE
Long-term trend (2000-2012)
Bay-wide: As a whole, Chesapeake Bay American shad abundance has steadily increased from 8.6 percent to 38.45 percent of the goal.
James River: Abundance has remained around 10 percent of the target, with a peak of 14 percent in both 2003 and 2011 and a low of 2 percent in 2006. Abundance estimates for the James River are a weighted combination of the upper James (Boshers Dam) and lower James data.
Potomac River: Unlike the other rivers, the Potomac’s abundance measurement is a running geometric mean calculated for all years since 1999. Abundance has steadily increased from 12.4 percent to 119.5 percent of the target.
Rappahannock River: Abundance peaked to approximately 90 percent of the target in 2003 and 2004, declined to a minimum of less than 30 percent in 2010and peaked again to approximately 90 percent in 2012.
Susquehanna River: Abundance has remained minimal at less than 1 percent of the target. Only a small portion of the shad that pass Conowingo Dam reach and pass York Haven Dam. There is optimal spawning habitat above York Haven Dam.
York River: Abundance reached a peak of 75 percent of the target in 2001 then stabilized at approximately 50 percent. Since 2005, shad abundance has declined to levels between 20-30 percent of the target.
Change from previous year (2011-2012)
Bay-wide: Increased from 35 percent to 38.5 percent of goal achieved.
James River: Decreased from 14.3percent to 9.6 percent of the target. Abundance estimates for the James River are a weighted combination of the upper James (Boshers Dam) and lower James data.
Potomac River: Increased from 103.2 percent to 119.5 percent of the target (32 to 36.6 CPUE)
Rappahannock River: Increased from 82.9 to 92.7 percent of the target.
Susquehanna River: Remained below 1 percent of the target (increased from 0 to 224 shad passing York Haven Dam)
York River: Decreased from 26.3 percent to 18.2 percent of the target (decreased from 4.6 to 3.2 CPUE)
Changes Made to This Indicator in 2013
New goals were established for the Virginia tributaries (York, Rappahannock, Lower James).
Changes were made to the data.
The weighting scheme for the baywide indicator was changed from weighting by catch to weighting by watershed size.
A new dynamic map on the indicator webpage features:
American Shad Restoration
Three of the rivers (James, Potomac and Susquehanna) have fish passage systems in place so shad can bypass dams and other blockages.
Several challenges persist for restoration of American shad. American shad use the Chesapeake Bay for spawning and nursery habitat, and reside along the Atlantic Coast (outside the Bay) for most of their life. If the shad abundance trend reverses from increasing to decreasing, this suggests that there may be factors external to Chesapeake Bay affecting American shad such as predation influences and/or bycatch in coastal fisheries.
American Shad Restoration Goals
The James River restoration goal of 500,000 American shad above Boshers Dam is based upon the number of shad that can be supported by the 137 miles (11,930 acres) of habitat that became available following construction of the Boshers Dam fishway.
The Susquehanna River restoration goal of two million American shad above the York Haven Dam was developed for the 1981 FERC hearings during hydro-project relicensing.
Benchmark restoration goals established via the 2007 ASMFC American Shad Stock Assessment are the targets for each tributary.
American Shad Abundance Data
The Susquehanna and James river counts are determined by fish passage data at York Haven and Boshers Dams, respectively.
Values for the lower James, Rappahannock and York rivers are determined using gill-net data from the Virginia Institute of Marine Science. Values for the Potomac River are determined using pound net bycatch and discard data from the Potomac River Fisheries Commission. To determine goal achievement, the 1950s commercial Catch per Unit Effort (CPUE) is compared to the current commercial (Potomac River pound net) or fishery-independent CPUE monitoring.
The number of shad passed at the York Haven and Boshers dams and the CPUE of shad caught via gill net and pound net are long term datasets that can be used for comparison with data from previous time periods. The data trends inform managers where efforts have been successful further study and restoration efforts are needed. Furthermore, these data are collected for other multi-jurisdictional management needs making these monitoring efforts relatively cost effective.
National Oceanic and Atmospheric Administration (NOAA)
Chesapeake Bay Program