Operational Plan for the Restoration of Diadromous Fishes to the ...

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Results of Tasks 20.1.3 and 20.2.2 should provide the bulk of necessary information to identify and prioritize stream connectivity limitations for alewife and American eel. 20.3.2 Undertake Stream Connectivity Improvements for Juvenile and Adult Alewife and American Eel Once tasks 20.1.3, 20.1.4, 20.2.1, 20.2.2, and 20.3.1 are completed, resources can be allocated and stream connectivity problems for juvenile and adult alewife and American eel remediated. 21.1.1 Develop a Memorandum of Understanding (MOU) with MDIFW for Selectively Removing Non-Native/Undesirable Fish Species at Fishway Passage Trapping Locations Prior to Removal of the Veazie and Great Works Dams An MOU between MDIFW and MDMR is needed to identify which non-native and undesirable fish species are to be removed from the Penobscot River at the Veazie and Mattaceunk fishway traps. If traps are installed at other fishways, then MOUs need to be developed for these trappings locations. 21.1.2 Develop a Memorandum of Understanding (MOU) with MDIFW for Selectively Removing Non-Native/Undesirable Fish Species at the Milford Fish Lift Sorting Facility (Post Veazie and Great Works Dam Removals) An MOU between MDIFW and MDMR is needed to identify which non-native and undesirable fish species are to be removed from the Penobscot River at the Milford fish lift sorting facility after the Veazie and Great Works dams are removed. Specifics will be outlined in the Milford Fish Lift Operating Protocols developed in Task 19.1.6. 21.1.3 Establish List of Non-Native/Undesirable Fish Species and Protocols for Removing or Allowing Passage at Fish Passage Facility Trapping Locations Non-native and undesirable fish species can be trapped at fishway traps as part of fish enumeration and brood stock collection operations. To prevent unintentional range expansion of non-native and undesirable fish species located downstream of fishway traps but not upstream, a list of fish species to be removed and protocols for removal will be established. For non-native and undesirable fish species already present upstream of trapping locations, protocols for removing or allowing passage will be established. 21.1.4 Undertake with Other Resource Agencies Risk Assessments of Range Expansion for Non-Native/Undesirable Fish Species Installing and/or operating fish passage facilities without appropriate controls can increase range expansion of non-native/undesirable fish species. This task is a placeholder within the Passage and Connectivity section. See Section 4 “Non- Native Species Including Northern Pike”, Tasks 23.1.2 and 23.1.3 for specific deliverables. PRFP Page 80
21.1.5 Develop Memorandum of Understandings with Resource Agencies and Fish Passage Facility Operators to Prevent Upstream Movements of Non- Native/Undesirable Fish Species Once Tasks 21.1.3 and 21.1.4 are complete, agreements with resource agencies and fish passage facility operators will be instituted at fish passage facilities where traps are currently being operated. 21.2.1 Assess with Other Resource Agencies the Need for Physical and/or Temporal Modifications to Fish Passage Facilities Structural modifications to existing fish passage facilities and/or temporal operation can lessen the opportunity for range expansion of non-native/undesirable fish species. However, modifications and/or temporal operation can impact movements of target restoration species. This task is a placeholder within the Passage and Connectivity section. See Section 4 “Non-Native Species Including Northern Pike”, Tasks 23.1.1.1, 23.1.1.3 and 23.1.1.3 for specific deliverables. 21.2.2 Obtain Funding to Trap or Seasonally/Permanently Modify Fish Passage Facilities to Prevent Upstream Movement of Non-Native/Undesirable Fish Species Once risks assessments and the need for physical and/or temporal modifications to fish passage facilities are completed (Tasks 21.1.4 and 21.2.1), it may be necessary to seasonally modify or trap fish passage facilities to prevent upstream movements of non-native/undesirable fish species. At other fish passage facilities, it may be necessary to permanently modify them to prevent upstream movements of nonnative/undesirable fish species. Specific mechanisms to fund modifications or traps will be identified should modifications or trapping of fish passage facilities be deemed necessary. References Abbott, A. 2008. Maine Road-Stream Crossing Survey Manual. Gulf of Maine Coastal Program. U. S. Fish and Wildlife Service. Falmouth, Maine. 27 pp. FERC (Federal Energy Regulatory Commission). 2004. Handbook for hydroelectric project licensing and 5 MW exemptions from licensing. Federal Energy Regulatory Commission, Washington, D.C. Hotchkiss, R. H. and C. M. Frei. 2007. Design for Fish Passage at Roadway-Stream Crossings: Synthesis Report. Office of Infrastructure Research and Development. Turner-Fairbank Highway Research Center. Federal Highway Administration. McLean, VA. MDOT (Maine Department of Transportation). 2008. Waterway and wildlife crossing policy and design guide. Third edition. Maine Department of Transportation, Augusta, ME. 122 pp. PRFP Page 81
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Operational Plan for the Restoratio
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Table of Contents Introduction ....
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Introduction The overarching goal o
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Section 1 - Alewife, American eel,
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Introduction Five species (shortnos
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3.0 Objective: Rebuild the rainbow
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Table 1. List of lakes above Veazie
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Figure 1. Alewife Phase 1 habitat (
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Table 2. River habitat that histori
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Work Plan Table The budget includes
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3.1.3, 3.2.1, and 3.3.1 Estimate th
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USFWS (Seavey). Analysis may includ
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A boat electrofishing survey (Yoder
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Table 5. Results of natural recolon
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Because adult shad mortality increa
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11.0 Rebuild the striped bass popul
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Page 35 and 36: Objective 12: Increase wild/natural
Page 37 and 38: Work Plan Table The budget includes
Page 39 and 40: 14.1.2 14.1.3 14.2.1 14.2.2 14.2.3
Page 41 and 42: 12.1.4 Operate the adult Atlantic s
Page 43 and 44: 12.6.1 Proposal to investigate natu
Page 45 and 46: the ability to target specific area
Page 47 and 48: occur. Assessment is likely to incl
Page 49 and 50: smolts needs to be documented (Task
Page 51 and 52: Section 2 - Passage and Connectivit
Page 53 and 54: Atlantic salmon. Two dams on the St
Page 55 and 56: On the tributaries, the downstream
Page 57 and 58: can prevent the successful downstre
Page 59 and 60: ensure maximum emigration of target
Page 61 and 62: 18.1.2 Strategy: Develop/conduct as
Page 63 and 64: 21.1.1 Strategy: Develop a Memorand
Page 65 and 66: 17.1.6 17.2.1 17.2.2 17.2.3 17.2.4
Page 67 and 68: 17.6.5 17.6.6 17.6.7 18.1.1 18.1.2
Page 69 and 70: 20.1.6 20.1.7 20.1.8 20.1.9 20.2.1
Page 71 and 72: Over the past 20 years, there have
Page 73 and 74: that address fish passage. Similarl
Page 75 and 76: 17.2.4 Assess Fish Passage Improvem
Page 77 and 78: 17.5.1 Review the FERC License and
Page 79 and 80: 18.1.1 Review Need and Process to I
Page 81 and 82: 19.1.4 Consult and/or Partner with
Page 83: goals, DMR will need to work with l
Page 87 and 88: Section 3 - Habitat PRFP Page 83
Page 89 and 90: Hydrology Riparian and organic inpu
Page 91 and 92: 22.8 Strategy: Undertake an IFIM to
Page 93 and 94: Work Plan Narratives 22.1 Expand US
Page 95 and 96: Recent surveys in coastal Maine riv
Page 97 and 98: Section 4 - Non-Native species incl
Page 99 and 100: 23.1.1.1.1.2 East Branch Pond, whic
Page 101 and 102: Investigate and maintain current bl
Page 103 and 104: The dam at Schoodic Lake has a 6’
Page 105 and 106: Work with IFW regional biologists t
Page 107 and 108: Authors: Joan Trial and Melissa Las
Page 109 and 110: Objective 28: Support regional and
Page 111 and 112: Coordinate data collection and shar
Page 113 and 114: Work Plan Narratives 26.1. Convene
Page 115 and 116: 27.5 Hold an interagency technical
Page 117 and 118: River Restoration Trust (PRRT or Tr
Page 119 and 120: Appendices Appendix A - Role of Hat
Page 121 and 122: Population Structure The ‘concept
Page 123 and 124: supplementation have been highly su
Page 125 and 126: 3. Blueback Herring Meristic/Morpho
Page 127 and 128: populations, Waldman et al. (1996)
Page 129 and 130: Summary No specific information is
Page 131 and 132: References Anderson, M.G., Vickery,
Page 133 and 134: Cumberland Basin, New Brunswick. Ph
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Table 1. Sub-drainage and reaches i
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itself verses mortality that may oc
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We estimated cumulative dam mortali
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Female Returns 16000 14000 12000 10
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that must be passed. Furthermore, h
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Appendix C - Penobscot Habitat and
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Parr density (no. / 100 m 2 ) 45 40
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Enfield Weldon to West Enfield Matt
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Habitat (units) Parr Production Hab
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Figure 8. Optimal parr production s
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Subwatershed Dam Reach Management R
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lakes fisheries: a general review a
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ecommended adjustments. While other
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Major flexibility constraints of th
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Table 6. Continued. YOY Parr Result
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Appendix E - Atlantic Salmon Fisher
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easonably be accessed; and 4) minim
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Approximately 600,000 smolts are st
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operations. Adult fish reared speci
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Methods We chose to divide the Peno
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• Measure 1b: Sub-drainages with
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Objective 3: Discontinue supplement
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� Strategy- Assess environmental
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Appendix G - Habitat Survey and Ass
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elated to diadromous fishes upstrea
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designs (GRTS), where samples are r
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with panels starting in year 1, 2,
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incorporate further refinements unt
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in statistical analyses stratum Str
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Appendix I - Downstream Passage Stu
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MILFORD (FERC No. 2534) Project Des
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Bangor-Pacific Hydro Associates. 19
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Shepard, S.L. and S.D. Hall. 1991.
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Options under the Multiparty Settle
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As a result of the discussion at th
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By 2000, PPL (new owner of the dams
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arriers to prevent movement of pike
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Kennebec 2008 WhittierPond Vienna N
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are a coldwater species and need ac
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Figure 4. Total species composition
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northern pike (Lucas 2008, Scott an
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Above1 Run 16.3 551 7 FLF, YLP, WHS
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any given water. During warmer peri
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In Maine, lake trout feed primarily
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Piscataquis drainage will likely of
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approximately 14°C”. These tempe
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cover, and aquatic macrophytes are
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and 2) the availability of data in
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Table 5 Northern Pike Waterway Habi
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4. The 40 largest watebodies in the
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5. About 97 percent of the rivers a
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Human-Caused Introductions Backgrou
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Table 7 Maine Lake Northern Pike Di
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Pattern of Introduction and Dispers
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4) The model developed by Solow and
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Inventory of Risk Rating for Waterb
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(Buck's Falls and Cowyard Falls), m
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Prescott Pond Little Wilson Stream
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Summary of Ecological Risk Introduc
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No improvements were made over the
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Level 3 Management actions These ar
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d. Conduct habitat surveys of the P
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Gallagher, M., R. Dill and G. Krame
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Starfield, A. M. and A. L. Bleloch.
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Appendix A: Trapping/Sorting/Counti
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means to “provide safe, timely an
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comprise the majority of fish passi
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exclusion. Information from publish
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A series TSCF system would route al
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(i.e., total exclusion of the targe
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PRFP Page 281
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PRFP Page 283
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Appendix B Outline for Preliminary
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channel would carry almost 1000 cfs
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powerhouse), rock weir/chevron/rest
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PRFP Page 291
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PRFP Page 294
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PRFP Page 296
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populations. Although each member s
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Appendix K - Northern Pike Movement
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MAINE DEPARTMENT OF MARINE RESOURCE
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Table of Contents (Cont’d) LIST O
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2.0 DESCRIPTION OF THE STUDY AREA 2
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3.0 METHODS Both streams were surve
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4.0 RESULTS 4.1 East Branch Lake 4.
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elevation) difference from the crib
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Figure 4: Water and Channel Elevati
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A portion of the stream passes to t
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4.1.3 Wangan and Sanborn brooks are
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Photo 6: View Looking Northwesterly
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location that would prevent fish fr
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APPENDIX 1 SURVEY OF NATURAL BARRIE
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Figure A-1: Orientation of Study Si
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Photo A-3: View from within Sanborn
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Response to Comments and Suggested
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Response: Early mortality syndrome
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population can provide 97,500 alewi
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DMR proposes to expand the Waldobor
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Salmon Comment: There are advocates
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Table 4. Species disposition Specie
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Kingsbury Pond X Long Pond X Long P
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Halfmoon Pond X Hammond Pond X X X
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West Garland Pond X West Lake X X X
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spread of any invasive species, and
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Response: There are conditions when
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Comment: Plan often uses the terms
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