River Herring: Assessment of Fish Passage Opportunities in Lower Hudson River Tributaries ( )

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River Herring: Assessment of Fish Passage Opportunities in Lower Hudson River Tributaries (2009-2012) Presentation to NY Region River Herring Workshop, HRF, Oct 22, 2012 Carl Alderson, NOAA Restoration Center Lisa Rosman, NOAA, Office of Response and Restoration

NOAA Funded Restoration Projects in the Northeast 216 salt marsh projects 206 fish passage projects Completed ~16,000 acres and ~1,400 stream miles Est ~4,0000 acres and ~ 1,500 stream miles planned

Northeast Fish Passage Prioritization Goal: to identify priority watersheds throughout the region to focus our fish passage projects Developed list of priority species among the 14 diadromous species in the region Mapped cooccurrence and ranked

Tributary Fish Passage Study of the Lower Hudson River Objectives Investigate Changes to Fish Passage Impediments Create an Inventory of Barriers for use as a Decision Making Tool Work with other agencies and programs to further mutual goals

Tributary Fish Passage Study of the Lower Hudson River Scope of Effort 65 Tributaries Update Prior Efforts (Schmidt et al 1996, Halavik and Orvis 1998, Machut et al 2007) o Not Limited to number of barriers per tributary Desktop Tools o Google Earth, Bing, Digital USGS 75 Series Topographic o Digital NYS Dam Inventory Groundtruthing: 51 of 65 tributaries all or partially field verified to date o GPS, Video, Photography, Notes

Tributary Fish Passage Study of the Lower Hudson River Proposed Actions Dam Removal and Culvert Upgrades (Preferred) Eelways, Fish Ladders, Rock Ramps (Less Preferred) No Action (eg, No Benefit, Owner Opposition, FERC Licensed, Regulatory Obstacle)

Evaluation of Barriers - Criteria for Determining Passability Presence/Absence of barriers and their physical attributes Challenges for anadromous and catadromous fish presented by barriers (passable part, all, or none, seasonal, tidally restricted) Stream gradient (steepness) Categorization of streams by hydrologic type (perennial, intermittent, or ephemeral)

Deliverables of the Study Database GIS IDENTIFYING LOCATION ATTRIBUTES RESTORATION ATTRIBUTES HABITAT ATTRIBUTES SPECIES ATTRIBUTES OBSTRUCTION ATTRIBUTES ACRE BENEFITS CONTACT ATTRIBUTES BIBLIOGRAPHY COMMENTS AND CONCERNS PHOTO LINKS Mapping Product Video Library Photo Library Development of Prioritization Tool

Study Scope: Sixty-five Lower Hudson Tributaries Annsville Creek Arden Brook Black Creek Breakneck Brook Catskill Creek Cedar Point Brook Cheviot Creek Claverack Creek Coeymans Creek Copper Mine Brook Coxsackie Creek Croton River Crows Nest Brook Crumb Elbow Dickey Brook Esopus Creek Fallkill Fallsburgh Creek Fishkill Creek Foundry Brook Furnace Brook Gordons Brook Hannacrois Creek Highland Brook Hunters Brook Indian Brook Indian Kill Kaaterskill Creek Kinderhook Creek Landsman Kill Lattintown Creek Maritje Kill Mill Creek (C) Mill Creek (R) Minisceongo Creek Moodna Creek Moordener Kill Muitzes Kill Murderers Creek Normans Creek Peekskill Hollow Brook Philipse Brook Pocantico River Poesten Kill Popolopen Brook Quassaic Creek Roeliff Jansen Kill Rondout Creek Roseton Brook Saw Kill Sing Sing Brook South Bay Creek South Lattintown Creek Sparkill Creek Sprout Brook Stockport Creek Stony Creek Twaalfskill Creek Vlockie Kill Vloman Kill Wades Brook Wallkill River Wappingers Creek Wickers Creek Wynants Kill

The NOAA Study Area Is: A subset of the overall Hudson watershed, defined by the outer most bounds of the historic, current and potential migratory routes of river herring, Shad and American Eel within the 65 tributaries of the Lower Hudson Estuary Partially Investigated Barriers Fully Investigated Barriers Partner agencies are also participating in the effort to restore diadromous fish runs, with some undertaking studies of their own NYSDEC Lower Hudson Watershed Studies NY/NJ Harbor Estuary Program Hudson Raritan Estuary Comprehensive Restoration Plan

The Tale of two NOAA led Barriers Studies within the Hudson Raritan Estuary Note the Spatial Patterns made by the Tributary barriers of the Hudson River in contrast with the barriers studied in the area of New York Harbor (Raritan, Passaic, Hackensack, Bronx Rivers and lesser tributaries) N The barriers in the New York Harbor Area are distributed throughout the low gradient rivers in the watershed, whereas the barriers studied on the Hudson Tributaries tightly cluster near the Hudson River main stem due to the steep terrain of the Hudson Valley

So many dams, but who is watching them? The New York State DEC Dam Safety Database NYSDSD Hazard Class A B C D Description Number of Dams in Study with Hazard Classification Low Hazard 51 Intermediate Hazard 18 High Hazard 13 Negligible or No Hazard 4 Of the 152 dams in our database, 86 are in NYSDSD 66 are not 86 Lower Hudson River Piermont to Beacon, NY Our Survey Dams consisting of natural and man-made barriers are shown in relation to some of the over 6000 dam records in the NYS Dam Safety Database but more than 10,000 dams are estimated to exist in NYS Nearly 800 dams in the Hudson River watershed The DSD categorizes dams by the hazard they present Hazard Rating refers to consequences of a dam's failure, not the condition of the dam

NOAA STUDY IN PROGRESS 2009-2012 51 Tributaries Visited 14 Tributaries NOT Visited 216 Barriers Field Visited 211 Stream Miles in the Survey 112 Barriers Not Visited 325 Average #Miles/Stream 65 Tributary Streams 328 Total Barriers 505 Average # Barriers per Tributary 064 Average distance in miles between barriers

And do (can) diadromous fish go beyond this point? For all 328 potential barriers, we asked, can diadromous fish potentially arrive at this point? 90 2 4 71 2 1 4 100 21 9 6 185 20 141 Yes No Seasonally Eel Only Limited TBD Passes All Diadromous No Passage Diadromous Seasonal Passage Diadromous Limited Passage Diadromous Tidally Passable Diadromous Limited Passage Anadromous Catadromous Passge TBD BARRIER EFFECTIVENESS Approximately 67 miles accessible to river herring

Probable Current Run Type Beyond Barrier 12 30 97 Diadromous 189 Eel only Resident Fish Only n =328 TBD BARRIER EFFECTIVENESS

Of the 328 barriers surveyed, we asked, what are the major categories present? 8 34 134 And, what is the first barrier to river herring on each of the 65 tributaries? 152 19 Natural Culverts/Bridges Dams TBD 38 7 1 BARRIER TYPES Dam Culvert Bridge Natural

Barren Land Deciduous Forest And, what is the land use/cover type? Developed High Intensity 6 1 56 32 17 3 1 18 1 64 70 18 29 1 Developed Low Intensity Developed Medium Intensity Developed Open Space Emergent Herbaceous Wetland Evergreen Forest Grassland_Herbaceous Mixed Forest 11 USGS LANDUSE DATA 2006 NA Open Water Pasture Hay LAND USE_COVER TYPE Shrub Scrub Woody Wetlands

Claverack Creek TODAY 1 FUTURE GOAL w/ dam removal 3 4 5 6 FUTURE GOAL EEL CLAVERACK CREEK Removal of dam 5 may allow eel to pass to RM 99 where the Claverack Creek Falls would present a significant challenge 7 CLAVERACK CREEK: The spillway of Dam #1 is approx 24 elevation above the elevation at the mouth It is a full barrier to fish passage Dam #2 is breached and does not effect passage Removal of Dams 1, 3 and 4 results in an additional 262 miles of passage for herring Removal of dams 1,3,4 would allow herring to pass to RM 45 where Dam #5 Stottsville Dam/Falls would present an obstacle to fish and a significant challenge eel even if removed

Sprout Brook FUTURE GOAL EEL TODAY 1 FUTURE GOAL w/ dam removal 4 3 SPROUT BROOK Removal of Dams 4-13 would allow free access to American Eel 13 SPROUT BROOK: Fish cannot pass beyond the 1 st dam Assuming that the Cortland Lake Dam ( #3 ) 37 in height remains in place, removal of Dams 1 & 2 results in no more than an additional 122 miles of passage for herring

Rondout Creek? FUTURE GOAL 2 w/ dam removal TODAY RONDOUT 1 RONDOUT CREEK: The 12 ft high Eddyville Dam (#1) stands at the head of tide Without removing the dam, fish would have no further access beyond the base of the dam Removal of Dam #1 would result in head of tide migration to 36 miles upstream Herring would likely pass to the natural ledges at RM 1110 (71 stream miles) Eel would continue an undetermined distance possibly to the next dam at RM 130

16 Tributaries where action can be prescribed Tributaries are eliminated where The first 16 man-made remaining barrier tributaries provides are no marked realistic as Tier opportunities 1 or Tier 2 These based include on the FERC quality and amount of benefits Sixty-five gained Lower Removal Hudson of all Tributaries: relicensing dams; 27 Tributaries dams and Where culverts First whose Barrier location, barriers is Man-Made size to herring and structure provides make an fish estimated passage 30 costly First miles Barrier with additional little is benefit; Either miles Natural dams of habitat and or culverts Removal Man-made that of are 1 st tier technically dams infeasible; provides and unrestricted those that access could to provide an estimated passage 196 to catadromous miles of habitat only Annsville Creek Arden Brook Black Creek Breakneck Brook Catskill Creek Cedar Point Brook Cheviot Creek Claverack Creek Coeymans Creek Copper Mine Brook Coxsackie Creek Croton River Crows Nest Brook Crumb Elbow Dickey Brook Esopus Creek Fallkill Fallsburgh Creek Fishkill Creek Foundry Brook Furnace Brook Gordons Brook Hannacrois Creek Highland Brook Hunters Brook Indian Brook Indian Kill Kaaterskill Creek Kinderhook Creek Landsman Kill Lattintown Creek Maritje Kill Mill Creek (C) Mill Creek (R) Minisceongo Creek Moodna Creek Moordener Kill Muitzes Kill Murderers Creek Normans Creek Peekskill Hollow Brook Philipse Brook Pocantico River Poesten Kill Popolopen Brook Quassaic Creek Roeliff Jansen Kill Rondout Creek Roseton Brook Saw Kill Sing Sing Brook South Bay Creek South Lattintown Creek Sparkill Creek Sprout Brook Stockport Creek Stony Creek Twaalfskill Creek Vlockie Kill Vloman Kill Wades Brook Wallkill River Wappingers Creek Wickers Creek Wynants Kill First Tier Dams Second Tier Dams 38 Natural Culvert Second Tier Culverts 27 Man-Made Dam

27 Tributaries Where First Barrier to Herring is Man-Made Arden Brook Black Creek Cheviot Creek Claverack Creek Copper Mine Brook Croton River Crows Nest Brook Dickey Brook Foundry Brook Furnace Brook Gordons Brook Kinderhook Creek Mill Creek (R) Minisceongo Creek Moodna Creek Murderers Creek Peekskill Hollow Brook Pocantico River Quassaic Creek Rondout Creek Roseton Brook South Bay Creek Sparkill Creek Sprout Brook Wades Brook Wallkill River Wynants Kill Culvert Dam

Sixty-five Lower Hudson Tributaries Black Creek Cheviot Creek Claverack Creek Croton River 16 Tributaries Where Action for Herring Likely Prescribed Tributaries were eliminated where first man-made barrier provides no realistic opportunities, eg, FERC relicensing dams; dams and culverts whose location, size and structure make fish passage costly with little benefit; culverts that are technically infeasible; and barriers that provide passage to catadromous eel only Furnace Brook Gordons Brook Minisceongo Creek Moodna Creek Peekskill Hollow Brook Pocantico River Quassaic Creek Rondout Creek South Bay Creek Sparkill Creek Sprout Brook Wynants Kill Culverts : to be ground truthed Dam

Based on the Quality and Amount of Benefits Gained Removal of all barriers to herring provides an estimated 30 miles additional miles of habitat Removal of 1 st tier dams provides unrestricted access for herring to an estimated 196 miles of habitat Black Creek Cheviot Creek Claverack Creek Croton River First Tier Dams Second Tier Dams Second Tier Culverts Furnace Brook Gordons Brook Minisceongo Creek Moodna Creek Peekskill Hollow Brook Pocantico River Quassaic Creek Rondout Creek South Bay Creek Sparkill Creek Sprout Brook Wynants Kill

Schmidt 1996 Halavick 1998 Comparison of Findings Tributary Barrier Schmidt Ranking Schmidt/Cooper Recommendation Halivak Ranking Halavik/Orvis Recommendation Rondout Dam 1 construct passage 1 install fish ladder, best opportunity Pocantico Dam 2 construct passage install fish ladder Coxsackie Falls 3 construct passage NA Not considered (not considered) Stockport (Claverack and Kinderhook) Rapids/Dams 4 remove rock at Stockport remove Claverack dam, doubts migratory fish reach Claverack and Kinderhook dams no action at Stockport Ledges and first dam on Kinderhook (FERC), Breach, notch, install fish ladder or remove first dam on Claverack Sparkill Dams 5 construct ladder, little evidence migratory fish spawn in this creek install fish ladder on both dams Muitzes Culvert 6 install baffles for passage at low tide no action Poesten Rapids 7 small amount of rock removal no action Wappinger Rapids/Falls 8 remove rock/widen passage NA Not considered (natural barrier) Quassaic Ledges/Dam 9 remove rocks; could remove or bypass dam but didn't think removal would open up much spawning area since not sure of numbers of migratory fish that arrive at this point citizen-led cleanups to extensive urban renewal of damaged riparian zone, breach or repair first dam Black Dam 10 Wynants Esopus Crumb Elbow Stop Log Control Dam on Top of Falls Dam on Top of Falls remove flashboards and debris or dam removal, not sure if migratory fish reach this barrier not ranked in top 10, not identified as first barrier not ranked in top 10, would require major passage project not ranked in top 10, not identified as first barrier, remove rocks from rapids, didn t think ladder on dam could be built due to height and steepness debris removal prior to and during spawning season curb non-point sources, clean up area, focus on mouth Install fish ladder for educational outreach Install fish ladder for educational outreach

Conclusions An estimate of the stream miles encompassing the full historic migratory routes of river herring could not be determined from the available historic data, due to the limited number and accuracy of historic investigations and accounts There are currently 67 tributary miles estimated available to river herring on the 65 tributaries of the Lower Hudson based on criteria of biological and physical limits of fish passage An estimated 30 tributary miles have the potential to be opened to river herring via dam removal, culvert upgrades or the placement of passage structures (ramps, ladders, bypass structures) Restoration opportunities (10 dams) on 4 tributaries (Claverack, Croton, Moodna, Rondout) could enhance access to habitat for an estimated 196 miles for river herring

What are the points to consider in a regional preassessment of multiple stream corridors w/multiple stream barriers? Even the high tech tools are blunt instruments Given limitations, pre-assessment provides a small subset of the data that will be required of a full feasibility study Consider the limitations of available data within five areas of Feasibility (Site Control, Political, Regulatory, Cost and Technical)

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