Session B8- Monitoring changes in diadromous populations resulting from fish passage improvements on the Acushnet River, Massachusetts

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University of Massachusetts - Amherst ScholarWorks@UMass Amherst International Conference on Engineering and Ecohydrology for Fish Passage International Conference on Engineering and Ecohydrology for Fish Passage 2011 Jun 29th, 1:55 PM - 2:15 PM Session B8- Monitoring changes in diadromous populations resulting from fish passage improvements on the Acushnet River, Massachusetts John Sheppard Massachusetts Division of Marine Fisheries Steve Block National Oceanic and Atmospheric Administration National Marine Fisheries Service Restoration Center Follow this and additional works at: http://scholarworks.umass.edu/fishpassage_conference Sheppard, John and Block, Steve, "Session B8- Monitoring changes in diadromous populations resulting from fish passage improvements on the Acushnet River, Massachusetts" (2011). International Conference on Engineering and Ecohydrology for Fish Passage. 30. http://scholarworks.umass.edu/fishpassage_conference/2011/june29/30 This Event is brought to you for free and open access by the The Fish Passage Community at UMass Amherst at ScholarWorks@UMass Amherst. It has been accepted for inclusion in International Conference on Engineering and Ecohydrology for Fish Passage by an authorized administrator of ScholarWorks@UMass Amherst. For more information, please contact scholarworks@library.umass.edu.

Monitoring changes in diadromous populations resulting from fish passage improvements on the Acushnet River, Massachusetts John J. Sheppard & Steve Block Presentation submitted to the National Conference on Engineering & Ecohydrology for Fish Passage Conference (June 27 29, 2011)

Participating Agencies Commonwealth of Mass. Department Fish & Game (MarineFisheries) United States Geological Survey National Oceanic & Atmospheric Administration Office of Habitat Conservation New Bedford Harbor Trustees Council United States Fish & Wildlife Service The Coalition for Buzzards Bay

Presentation Outline 1. The Study Area 2. Fish Passage Improvements 3. Biological Monitoring

1. Acushnet Cushea (Wampanoag) meaning as far as the waters 2. Stream Length 8.2 miles (3 rd order) 3. Diadromous species present: a. Alewife (Alosa pseudoharengus) 1. The study area: The Acushnet River b. Blueback herring (A. aestivalis) c. American eel (Anguilla rostrata) C d. Smelt (Osmerus mordax) e. Striped bass (Morone saxatilis) 4. USEPA Superfund National Priorities List 5. MADEP Priority Tier 1 disposal site B 303(d) Impaired Waters (CWA) 6. Three Main Obstructions: a. Acushnet Sawmill Dam b. Hamlin Street Dam c. New Bedford Reservoir Dam A

3. Fish Passage Improvements 1. New Bedford Reservoir Dam 2. Acushnet Sawmill Dam 3. Hamlin Street Dam

Fish Passage Improvements (cont.): New Bedford Reservoir Dam Lower Section River Mile: 8.1 Dam Type: Dam & elevation change Material: Granite with wooden boards Impoundment: 220 acres Upper Section Year Built: 1867 Owner: City of New Bedford Spillway Width: 50 feet Spillway Height: 11 feet

Fish Passage Improvements (cont.): New Bedford Reservoir Dam 2002: State-of-the-art denil fishway constructed Project cost: < $250,000

Fish Passage Improvements (cont.): New Bedford Reservoir Dam Fishway Design: Denil Material: Concrete with wooden baffles Length: 264 feet Inside width: 3 feet Outside width: 5 feet No. baffles: 26 Notch width: 21 inches Pool Length: N/A Condition: Excellent Functionality: Passable ( 12 14 cfs) Restoration of access to the 220-acre New Bedford Reservoir may result in an estimated potential population of over 240,000 river herring (based on 1,100 fish/acre)

Fish Passage Improvements (cont.): Acushnet Sawmill Dam River Mile: 4.4 Type: Dam Material: Concrete & stone Impoundment: Saw Mill Pond (9.5 acres) Mean flow(s): HEC-RAS (1-D): 25 cfs; 8.2 cfs (low); 1.0 cfs (drought) Year Built: 1746 (rebuilt in 1920) Owner: Acushnet Sawmill Co. Spillway Width: 118 feet Spillway Height: 4.6 feet Impairments: Nutrients, pathogens, organic enrichment, low DO, vegetation

Fish Passage Improvements (cont.): Acushnet Sawmill Dam Sawmill Dam fishway construction: July, 2007 Sawmill Dam fishway schematics (EA Engineering, Science & Technology) 1. Fishway Type: Constricted weir, rock step-pool (11 rock weirs, 10 pools) 2. Length of dam reduced, stream channel re-defined 3. Top of dam notched and lowered 3 feet 4. Eleven weirs constructed of large boulders (3,000 5,000 lbs. each) placed at different elevations allows fish to ascend/descend at most water levels

Fish Passage Improvements (cont.): Acushnet Sawmill Dam Pre-Construction Acushnet Sawmill Fishway (Autumn, 2005) Post-Construction Acushnet Sawmill Fishway (Autumn, 2007) A relatively new innovation which effectively eliminates dams without removal. Only a few exist on the east coast (first in the Commonwealth).

Fish Passage Improvements (cont.): Hamlin Street Dam River Mile: 5.3 Type: Dam Material: Concrete with wooden boards Impoundment: 12.5 acres Year Built: 1920 Owner: Town of Acushnet Spillway width: 4.7 feet Spillway Height: 1.7 feet

Fish Passage Improvements (cont.): Hamlin Street Dam Hamlin Street Fishway Schematic (EA Engineering, Science & Technology) Hamlin Street Fishway (May, 2008) Similar structure built at Hamlin Street to overcome smaller elevation differential (5 rock weirs, 4 pools) Total cost (Sawmill and Hamlin Street fishways) = $1.2 million

4. Biological Monitoring 1. River herring 2. American eel

Biological Monitoring (cont.): River herring sampling results SUMMARY Year Deployed Removed N (sp.) N (ale) N (bbh) % (sp.) Peak obs. 2005 4/25 6/10 543 (8 sp.) 395 0 73 5/3 5/6 2006 4/11 6/29 353 (8 sp.) 202 0 57 4/25 4/28 2007 3/29 6/29 446 (8 sp.) 366 0 87 4/23 4/27 2008 3/31 6/6 1,119 (9 sp.) 977 1 87 4/10 5/1 2009 3/30 6/5 1,835 (8 sp.) 1,695 5 93 4/19 5/2 2010 3/29 6/3 2,980 (10 sp.) 2,703 7 91 4/6 5/4 2011 3/29 6/3 3,761 (11 sp.) 3,608 71 98 4/8 5/2 5/14 5/16

Biological Monitoring (cont.): Elver sampling results Sawmill Reservoir Year Period N( YOY ) N( 1+ ) Mean CPUE N( YOY ) N( 1+ ) Mean CPUE Peak Period 2005 4/11 6/10 1,284 (100%) 0 1.37 0 (0%) 1 0.001 4/20 4/29 5/10 5/17 2006 3/29 6/6 427 (100%) 0 0.55 5 (10%) 43 0.06 4/11 5/5 2007 3/27 6/15 180 (100%) 0 0.18 0 (0 %) 12 0.01 4/9 4/18 5/2 5/9 2008 4/1 6/6 4,635 (99%) 2 5.2 719 (92%) 65 0.79 4/9 4/18 5/2 5/9 2009 3/31 6/5 5,904 (99%) 3 7.0 104 (61%) 64 0.2 4/10 4/30 5/5 5/28 2010 3/29 6/4 3,330 (99%) 4 3.3 0 (0%) 54 0.05 4/7 4/23 4/30 5/4 2011 3/28 6/3 8,365 (99%) 3 7.4 85 (49%) 89 0.2 3/30 4/28

Biological Monitoring (cont.): Summary Observations 1. Results suggest new fishways have resulted in improved access to spawning and nursery habitat (New Bedford Reservoir) for river herring 2. Increased recruitment of elvers into the watershed during the postconstruction period 3. In particular, YOY elvers have access to the upper watershed (increased numbers present in samples)

Acknowledgements 1. MarineFisheries staff Phillips Brady, Ed Clark, Luis Carmo, Derek Perry, David Kowalske, Joe Fascendola, Dan Syriala, Josh Black, Talia Bigelow, Andrea Petrella, Jeff Devine, Kelly Kleister 2. Tony Williams and staff (Coalition for Buzzards Bay) 3. Dr. Alex Haro (USGS)