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American Shad Migration in the Westfield River, MA: Is Wastewater an Issue?. Nathan Henderson B. Shreve-Gibb J. Pearson D. Billips. Project Support. City of Westfield, MA . Presentation Outline. Introduction Project Background Permitting requirements for expansion
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American Shad Migration in the Westfield River, MA:Is Wastewater an Issue? Nathan Henderson B. Shreve-Gibb J. Pearson D. Billips
Project Support City of Westfield, MA
Presentation Outline • Introduction • Project Background • Permitting requirements for expansion • NPDES permit provision fish tagging study • Westfield River fish restoration • Methods • Fish Tagging • Radio Telemetry • Water Quality Sampling • Results (2002, 2004) • Radio Telemetry • Fish Tagging • Water Quality Sampling • Conclusions
Project Background • Water Pollution Control Plant (WPCP), City of Westfield (1973) • Project Evaluation Report (PER) 1998 detailed upgrade • 50 percent expansion to treat up to 6.1 mgd • Draft Environmental Impact Report (DEIR) in 2000 • Comments from state and federal agencies indicated concern • During low flow, a zone of plume-free passage for anadromous fish may not exist in the Westfield River • Fish passage required additional investigation • Dye study conducted at 7Q10 (low flow) in 2000
Permit Provisions • Final EIR issued in 2000 • Dye study indicated zone of passage on southern side of island • NPDES permit provisions • required City of Westfield to: • Conduct a fish tagging study in an attempt to determine the effect of discharge on fish migration • Specifically American shad migration
Westfield River Fish Bypass Facility • DSI Dam in West Springfield • 7.0 miles downstream from outfall • Fishway completed in 1996 • Anadromous species reintroduced to upper watershed • 1,413 American shad (1996) • Peaked to 4,720 in 2001 • Recent declines to 1,237 in 2005 • Shad migration not known
Purpose of Study • Determine: Is there an issue related to outfall? • Collect data on shad passage past the WPCP outfall • Collect water quality data in association with fish passage • Use radio telemetry to track American shad upstream and through the Westfield WPCP mixing zone • Target worst case scenario (2002 study) • Low river flow where effluent mixing concentrations are highest • Target peak shad run (2004 study)
Island Methods • Radio telemetry • Combination of fixed and manual tracking receivers • 1 station located 300 meters downstream of outfall - 1 station located 50 meters upstream of outfall
Fish Tagging Methods • Shad were captured at the fish lift • Stomach tagging shad • Coded Lotek transmitter • Measured for length and condition
Monitoring • Manual tracking • Downloading fixed receivers • Water quality sampling • River water quality at two stations (upstream and downstream of outfall) • Effluent water quality one station • Parameters (total Cu, Dissolved Cu, TRC, NO3, NH3, Cd, Cond, pH, Temp, DO)
Results (2002) • Targeted low flow conditions below 300 cfs • 21 shad (10 females 11 males) • monitored for 30 days 30 Tagging date 25 Shad tagging date 6/19/02 20 15 10
Average Daily Discharge Over 86 Year Period Average start of shad run Average end of shad run
Results (2002) • High flows in spring 2002 • Shad tagged during end of migratory run • One week after tagging temperatures surpassed 20oC • Two fish approached and successfully passed outfall • All water quality parameters within acceptable limits • Remaining fish found in spawning habitat 2 - 5 miles below outfall • Regulatory agencies concluded a second study was necessary to further document shad migration
Results (2004) • Targeted peak of the shad run (900 cfs) • 20 fish were tagged in May and monitored for 3 weeks • 3 fish did not leave the forebay • 2 fish moved downstream after tagging • 15 fish entered study reach (between dam and outfall)
Shad Movement (2004) • 8 tagged fish passed outfall • 53% of shad that migrated into the study reach passed the outfall • 7 females and 1 male • 9.5 minutes to migrate past outfall • 1.5 miles upstream of discharge in ideal spawning habitat • No fish were found residing below the discharge • Remaining 7 fish were found in similar areas as 2002 study 2 - 5 miles below the outfall • Movement ranged from 0 to 7.3 miles per day
Water Quality and Flow (2004) • Flow averaged 524 cfs when 4 fish passed outfall • Cu, NO3, and NH3, slightly increased from upstream to downstream of outfall • Instream temperature averaged 15oC (20oC end of the study) • DO concentrations never fell below 8.25 mg/L • Temperature and DO were slightly lower in effluent than in river
Discussion • In 2002 and 2004 shad passed outfall • Water quality parameters affected by outfall did not affect shad movement • No fish resided below outfall • Habitat not suitable for spawning or holding • Long term exposure to plume concentrations not anticipated as shad move quickly through area • Flow and temperature most critical parameters affecting shad migration • 2004 flow was considered low when 4 fish passed outfall
Conclusions • American shad migration and spawning habitat was documented • Discharge did not represent a barrier to the migration of American shad in the Westfield River • USEPA and MA Division of Fish and Wildlife determined no further study was necessary • NPDES provisions met