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

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22.4 Use additional information and data to indicate habitat quality (temperature, gradients, drainage area etc.). 22.4 and 22.5 Review or acquire baseline water chemistry data in all critical habitats. 22.5 Condcut studies for other species to identify habitat 22.6 Develop method to assess key qualitative habitat features (embeddedness, substrate type, large wood, etc.) and systematically address these ideas. 22.6 Establish team to develop watershed assessment plan 2010 DMR $0 2011 DMR $0 2009-2014 DMR $250,000 2009-2014 DMR $250,000 2010 DMR and partners $0 22.6 Develop habitat protection/restoration plan 2011+ DMR and partners $25,000 22.6 Conduct a basin-wide watershed assessment per Roni et al.( 2002). 2009-2014 DMR $250,000 22.6.1 Examine the factors limiting Atlantic salmon juvenile production at Katahdin Iron Works area on the Pleasant River. 2010 DMR $0 22.7 Revisit the water management plan for the one major water control structure in the drainage $0 Grand Lake Matagamon 2010 DMR/DEP 22.8 Undertake an IFIM to pinpoint seasonally habitat protective flows 2010 DMR $0 22.9 Remove or repair roads that impair Annaul watershed processes DMR/DOT/MFS $1,000,000 22.10 Support studies of MDN inputs to the basin (see Issue 7) Annual DMR/NOAA $0 22.11 Identify areas for riparian forest improvement and pursue improvements. 22.11 and 22.12 Complete restoration/protection projects 22.12 Increase complexity by adding large wood or boulders 22.12.1 Predict LWD loadings in other streams using an LWD loading model based on forest stand data, environmental variables, and stochastic events. 22.13 Use PITS model to set restoration goals Annual DMF/IFW/MFS $25,000 Annual DMR/NGOs $2,500,000 Annual DMR/IFW/MFS $500,000 2010 DMR/USFS/MFS $45,000 2010 NOAA $0 PRFP Page 88
Work Plan Narratives 22.1 Expand USFWS barrier model by adding existing layers. 22.2 Develop GIS model(s) to predict the location and amount of Atlantic salmon habitat in the watershed within 3 years. In smaller watersheds, salmon habitat typically has been mapped and identified by foot or boat survey or on-the-water surveys. This approach is not practical for the Penobscot watershed, which is the largest in Maine. The development of GIS model(s) to predict the location and amount of Atlantic salmon habitat will provide more information faster (with estimates of precision) at lower cost than surveys of the entire watershed. Model out puts will be verified with existing data. 22.3 Conduct expanded DMR “Big River” physical habitat surveys to provide data to verify the salmon GIS model(s). Field surveys of habitat should continue to use the DMR BSRFH “Big River” habitat survey method and focus on waters of importance to salmon management, but also focus on surveying a diversity of stream types (size, gradient, geographic location). Expand the survey to include observation on large wood, connectivity, embeddedness, substrate type, etc. This will help managers understand the scope and frequency of habitat across various stream types. Such surveys will also help to validate modeling efforts, providing more and faster habitat information with estimates of precision at lower cost. A sampling plan for habitat survey will be established by biologists familiar with the basin and with the GIS habitat model. Such a survey may include stream reaches randomly chosen for a defined sampling frame. On an annual basis, a portion of each summer will be allotted to habitat survey, with balance between habitat assessment and survey. 22.4 Maintain or expand water temperature measurements in salmon habitat. Water temperature monitoring in the Penobscot basin falls within a larger state-wide water temperature monitoring plan for Atlantic salmon waters. Recently, DMR BSRFH has been scaling back the number of temperature loggers deployed annually, and is concentrating on monitoring key index sites and using additional loggers to rotate among sites for interest. This correlates water temperatures at new sites to the index site(s) and allows a prediction model to be constructed. Water temperature should continue to be recorded at index sites, while additional loggers shall be deployed at sites of interest. New sites may be chosen using a GTRS method. This will provide unbiased water temperature information for the basin. The amount of effort to put into water temperature monitoring should be kept at or below current levels, unless a well-defined study is put forth. More effort should be put into analysis and interpretation of water temperature data. Notably, a stream classification system should be finalized and put into general use statewide. 22.5 For other species conduct studies (e.g. telemetry, hydroacoustics) or survey (e.g. visual or auditory) to identify spawning, nursery, feeding, and overwintering habitat as appropriate. PRFP Page 89
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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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meta-population. Based on watershed
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Objective 12: Increase wild/natural
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Work Plan Table The budget includes
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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 and 84: goals, DMR will need to work with l
Page 85 and 86: 21.1.5 Develop Memorandum of Unders
Page 87 and 88: Section 3 - Habitat PRFP Page 83
Page 89 and 90: Hydrology Riparian and organic inpu
Page 91: 22.8 Strategy: Undertake an IFIM to
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
Page 135 and 136: Table 1. Sub-drainage and reaches i
Page 137 and 138: itself verses mortality that may oc
Page 139 and 140: We estimated cumulative dam mortali
Page 141 and 142: 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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