Biological Opinions - Bureau of Reclamation

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8.3.6 Effects to Habitat for Larvae and Age-0 Juveniles ................................................. 154 8.3.7 Effects to the SNS in Gerber Reservoir .................................................................. 158 8.3.8 Effects to the LRS and the SNS in Tule Lake Sump 1A ........................................ 162 8.3.9 Effects to LRS and the SNS in the Lost River ........................................................ 165 8.3.10 Summary of Effects of the Proposed Action to LRS and SNS in the Lost River Subbasin Recovery Unit ..................................................................................................... 167 8.4 Effects of Proposed Project Operation and Maintenance Activities ........................... 168 8.4.1 Effects of Clear Lake Dam Maintenance ................................................................ 168 8.4.2 Effects of A Canal Headworks Maintenance and Canal Salvage ........................... 168 8.4.3 Effects of Lost River Diversion Channel Maintenance .......................................... 169 8.4.4 Effects of Link River Dam Fish Ladder Maintenance ............................................ 169 8.4.5 Effects of Maintenance to Other Project Canals, Laterals, and Drains .................. 170 8.4.6 Effects of Right-of-way and Access Maintenance .................................................. 170 8.4.7 Effects of Water Measurement Gage Maintenance ................................................ 171 8.4.8 Summary of Effects of Proposed O&M Activities to LRS and SNS ..................... 171 8.5 Effects of the Proposed Conservation Measures ........................................................ 171 8.5.1 Canal Salvage.......................................................................................................... 172 8.5.2 Controlled (Captive) Propagation ........................................................................... 172 8.5.3 Capture of Adult Suckers in Lake Ewauna Reservoir and Relocation to UKL ...... 174 8.5.4 Effects of Recovery Implementation Team Participation ....................................... 174 8.5.5 Summary of Effects to LRS and SNS from Proposed Conservation Measures ..... 175 8.6 Cumulative Effects - Lost River Sucker and Shortnose Sucker ................................. 175 9 LOST RIVER SUCKER AND SHORTNOSE SUCKER CRITICAL HABITAT ............ 177 9.1 Status and Environmental Baseline of Critical Habitat .............................................. 177 9.2 Analytical Approach and Role of Critical Habitat in LRS and SNS Recovery .......... 180 9.3 Effects of Proposed Project Operations to LRS and SNS Critical Habitat ................. 181 9.3.1 Effects to LRS and SNS Critical Habitat Unit 1 ..................................................... 181 9.3.2 Effects to LRS and SNS Critical Habitat Unit 2 ..................................................... 184 9.4 Cumulative Effects to Critical Habitat ........................................................................ 188 10 LRS AND SNS INTEGRATION AND SYNTHESIS (Jeopardy and Destruction or Adverse Modification Determinations) ..................................................................................................... 189 10.1 Range-wide Status of the LRS and SNS and Their Environmental Baseline in the Action Area ............................................................................................................................. 189 10.2 Summary of Effects UKL Recovery Unit ................................................................... 190 10.3 Summary of Effects to the Lost River Basin Recovery Unit ...................................... 192 10.4 Effects to LRS and SNS Population Viability ............................................................ 193 10.5 Conclusion for LRS and SNS ..................................................................................... 196 10.6 Basis for the Conclusion Regarding Jeopardy for LRS and SNS ............................... 196 10.7 Basis for the Conclusion Regarding Destruction or Adverse Modification of Critical Habitat 197 11 SONCC COHO SALMON CRITICAL HABITAT ........................................................... 199 11.1 Analytical Approach ................................................................................................... 199 11.1.1 Overview of NMFS’ Assessment Framework ........................................................ 199 11.1.2 Concept of the Natural Flow Regime ..................................................................... 201 11.1.3 Flow and Rearing Habitat Analysis ........................................................................ 202 11.1.4 Evidence Available for the Consultation ................................................................ 206 iii
11.1.5 Critical Assumptions ............................................................................................... 206 11.2 Status of SONCC Coho Salmon Critical Habitat ....................................................... 207 11.2.1 Current Condition of Critical Habitat at the ESU Scale ......................................... 208 11.2.2 Factors Affecting SONCC Coho Salmon Critical Habitat ..................................... 210 11.3 Environmental Baseline of Coho Salmon Critical Habitat in the Action Area .......... 214 11.3.1 Habitat Conditions in the Action Area .................................................................... 215 11.3.2 Upper Klamath River Reach ................................................................................... 219 11.3.3 Middle Klamath River ............................................................................................ 221 11.3.4 Shasta River ............................................................................................................ 223 11.3.5 Scott River .............................................................................................................. 224 11.3.6 Salmon River .......................................................................................................... 227 11.3.7 Summary of Critical Habitat in Interior-Klamath Diversity Stratum ..................... 228 11.3.8 Factors Affecting Coho Salmon Critical Habitat in the Action Area ..................... 228 11.4 Effects to SONCC Coho Salmon ESU Critical Habitat.............................................. 247 11.4.1 Project Operations ................................................................................................... 247 11.4.2 Restoration Activities.............................................................................................. 278 11.5 Cumulative Effects...................................................................................................... 287 11.5.1 Control of Wildland Fires on Non-Federal Lands .................................................. 287 11.5.2 Klamath River Basin Adjudication ......................................................................... 288 11.5.3 Residential Development and Existing Residential Infrastructure ......................... 288 11.5.4 Recreation, Including Hiking, Camping, Fishing, and Hunting ............................. 289 11.5.5 Total Maximum Daily Loads .................................................................................. 289 11.6 Integration and Synthesis ............................................................................................ 289 11.6.1 Condition of Critical Habitat at the ESU Scale ...................................................... 290 11.6.2 Condition of Critical Habitat in the Interior Klamath Diversity Stratum ............... 290 11.6.3 Project Effects on Essential Habitat Types ............................................................. 291 11.6.4 Response and Risk to the SONCC Coho Salmon ESU Critical Habitat................. 294 11.7 Conclusion .................................................................................................................. 294 12 SONCC COHO SALMON ESU ........................................................................................ 295 12.1 Analytical Approach ................................................................................................... 295 12.1.1 Overview of NMFS’ Assessment Framework ........................................................ 295 12.2 Status of the Species ................................................................................................... 300 12.2.1 Life History ............................................................................................................. 300 12.2.2 Distribution ............................................................................................................. 301 12.2.3 Conservation Needs of the Species ......................................................................... 302 12.2.4 Extinction Risk Criteria .......................................................................................... 303 12.2.5 Status and Trend ..................................................................................................... 305 12.2.6 Factors Responsible for the Current Status of SONCC Coho Salmon ESU .......... 313 12.3 Environmental Baseline of Coho Salmon in the Action Area .................................... 320 12.3.1 Periodicity of Coho Salmon in the Action Area ..................................................... 320 12.3.2 Risk of Extinction of Klamath Populations ............................................................ 325 12.3.3 Factors Affecting Coho Salmon in the Action Area ............................................... 329 12.4 Effects to Individuals .................................................................................................. 336 12.4.1 Project Operations ................................................................................................... 336 12.4.2 Restoration Activities.............................................................................................. 356 12.5 Cumulative Effects...................................................................................................... 366 iv
Page 1 and 2: National Marine Fisheries Service U
Page 3: 7.4.5 LRS and SNS Population Dynami
Page 7 and 8: 16 APPENDICIES ....................
Page 9 and 10: Table 8.2 UKL end-of-month elevatio
Page 11 and 12: LIST OF FIGURES Figure 3.1. The act
Page 13 and 14: Figure 11.17. Coho salmon fry habit
Page 15 and 16: ABBREVIATIONS AND ACRONYMS Abbrevia
Page 17 and 18: Abbreviation/Acronym YTEP WDFW WRIM
Page 19 and 20: In 2001, the Services issued BiOps
Page 21 and 22: Findings of Fact and Order of Deter
Page 23 and 24: proposed changes to the vegetation
Page 25 and 26: Figure 3.1. The action area for Rec
Page 27 and 28: 4 PROPOSED ACTION Reclamation propo
Page 29 and 30: 4.2 Element Two Operate the Project
Page 31 and 32: October 1 and March 1. The proposed
Page 33 and 34: Reclamation incorporated the 1981 t
Page 35 and 36: Provide Project irrigation deliveri
Page 37 and 38: Table 4.3. UKL fill rate adjustment
Page 39 and 40: Table 4.5. Calculation of fall/wint
Page 41 and 42: Flows below IGD are ultimately the
Page 43 and 44: The EWA, Project Supply, and UKL Re
Page 45 and 46: Table 4.8. Environmental Water Acco
Page 47 and 48: eleases somewhat on the ascending l
Page 49 and 50: fish disease, die off, entrainment,
Page 51 and 52: acre-feet when the Project Supply c
Page 53 and 54: Table 4.11. Monthly maximum Lower K
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4.2.4 Ramp-Down Rates at Iron Gate
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progresses and EWA volumes are upda
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O&M activities are carried out eith
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1. The A Canal has six headgates th
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Therefore, Reclamation proposes to
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coordinate with the NMFS to develop
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the confluence with Omogar Creek at
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though several major improvements t
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Sucker larvae transform into age-0
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units: (1) Clear Lake; (2) Tule Lak
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Figure 7.2. Adult spawning populati
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Table 7.1. Estimated LRS and SNS ad
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1905, Ch. 567, 33 Stat. 714). The P
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Figure 7.4 Modeled April through No
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7.9.2 Klamath Basin The Oregon Clim
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A change in mean precipitation rang
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Table 7.2 Impaired water bodies wit
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Table 7.3 Seasonal comparisons of p
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ammonia that is lethal to 50 percen
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Table 7.4 Estimated external phosph
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examination of juvenile suckers fro
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Evaluation of baseline hydrology in
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2012 1931 through 2012 12.6% 0.24 5
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The overall water year trend (Table
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Figure 7.7 Sprague River trends, wa
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Figure 7.9 Sprague River trends, wa
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Figure 7.12 Williamson River trends
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Figure 7.14 UKL trends, water years
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Figure 7.17 UKL: net inflow departu
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7.10.3.3 Competition and Predation
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By late July, surviving larval suck
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Threat Nature of Threat Life Stage
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2011) and increased adult spawning
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Based on the best available informa
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contrast, water levels began 1.5 ft
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evaporation and seepage estimated a
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prolonged low oxygen conditions if
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The April through September 4,034.6
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8 EFFECTS OF THE ACTION ON LOST RIV
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Although the volume of Project wate
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than 1 m), and fitting one or more
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Figure 8.3. UKL elevations at the e
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Services and Reclamation will deter
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For cumulative net inflow values be
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Figure 8.8. UKL elevations at the e
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Figure 8.10. UKL elevations at the
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Figure 8.12. UKL elevations at the
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natural and man-caused changes in i
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Table 8.1 UKL end-of-month surface
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UKL. Based on best available inform
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larvae in UKL. Annual production of
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Table 8.5 UKL end-of-month elevatio
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Based on our review of the literatu
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into the Pelican Bay water quality
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We assume that UKL surface elevatio
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vary by several orders of magnitude
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survival rates, we know that some o
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populations, and contains the large
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8.3.5.1 Effects to Adult Sucker Spa
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Table 8.8 Clear Lake surface elevat
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occur, especially in the west lobe.
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Table 8.9 End of the month surface
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8.3.7.4 Effects of Entrainment Loss
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The source of the sediment is unkno
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period when they migrate upstream t
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limited LRS and SNS persistence in
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term and localized and because fish
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8.5.1 Canal Salvage Reclamation pro
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high predation rates and failure of
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include the Klamath Basin Rangeland
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Figure 9.1 Designated CHUs for the
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These are discussed in greater deta
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The proposed action will have no ef
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No other spawning habitat exists be
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consulted on. Current monitoring da
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proposed action and this PCE suppor
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Because of a multi-decade lack of r
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Adverse effects of the proposed act
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that juvenile survival is most like
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elocation effort in Lake Ewauna to
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LRS and SNS population resiliency o
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stratum 4 (Interior Klamath) in whi
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Pacific salmonids Oncorhynchus spp.
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scenario, actions and elements of t
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flow prescriptions should mimic pro
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11.2.1 Current Condition of Critica
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11.2.2 Factors Affecting SONCC Coho
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e disoriented or displaced downstre
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enhancement, and rehabilitative act
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Water Temperature Sedimentation Org
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Figure 11.1 Longitudinal and season
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functioning floodplains that fail t
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downstream of IGD, (2) enhance coho
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few local ranchers and water distri
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in some tributaries, access to and
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11.3.7 Summary of Critical Habitat
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these two time periods, the effects
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consists of approximately 29,000 ac
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The PacifiCorp habitat conservation
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IGD, or used in constructed habitat
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estoration, watershed planning, sal
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Table 11.4. Modeled suspended sedim
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parasites Ceratomyxa shasta (causes
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that become infected is estimated t
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where snow water equivalent is proj
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minimizing disease risks, the detai
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Figure 11.4. Proposed action, histo
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Figure 11.6. Proposed action weekly
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Figure 11.9. Regression between EWA
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Figure 11.11. Proposed action and o
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Figure 11.12. Number of days per wa
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Figure 11.14. Monthly coefficient o
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IGD. The proposed action modeled da
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The results from Table 11.7 indicat
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likely to increase the quantity of
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habitat decreases between the Shast
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Table 11.9. Daily average mainstem
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Table 11.10. Daily average mainstem
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5% 3336 13176 27664 26168 30946 237
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The proposed action results in agri
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Figure 11.21. Monthly mean of daily
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Riparian restoration projects will
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expected to be typical riparian spe
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Table 11.13. Annual percent of proj
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esource needs as they grow, and 3)
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11.5.2 Klamath River Basin Adjudica
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coho salmon within the Klamath Rive
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aspects of a natural flow regime th
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element of coho salmon critical hab
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12.1.1.1 Risk Analyses for Endanger
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ESU DIVERSITY STRATA POPULATIONS IN
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eproduction, and distribution. The
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Figure 12.2. Historic population st
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the average ratio of IP-km to total
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Although long-term data on coho sal
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1980 1981 1982 1983 1984 1985 1986
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maintain viable abundances in many
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12.2.5.5 Viability Summary Though p
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coastal currents and upwelling, kno
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12.2.6.2 Marine Derived Nutrients M
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fisheries south of Cape Falcon, Ore
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12.3 Environmental Baseline of Coho
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water temperatures up to 19 ºC in
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some coho salmon smolts may stop mi
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threshold, all Klamath River coho s
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abundance threshold (Table 12.3). T
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mainstem Klamath and Trinity rivers
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Although there are risks to Klamath
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activities are generally beneficial
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12.4 Effects to Individuals The pro
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12.4.1.2 Response 12.4.1.2.1 Adults
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(2012) believes is representative o
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genotype II density of 5 spores/L w
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flows provide a limit to the increa
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polychaete and sediment disturbance
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which will likely result in a relat
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etween Trees of Heaven (RM 172) and
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action. Reclamation estimated that
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Based on literature, increased comp
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Table 12.6. Summary of risks result
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most juveniles. Stream flow diversi
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at most fish relocation sites, base
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higher, the minimally increased sed
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Small pulses of moderately turbid w
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Boulder faces in the deflector stru
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conditions may fail if those condit
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Adverse effects of the proposed act
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Potential Stressor Habitat Reductio
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Potential Stressor Elevated water t
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12.6.2 Effects of fitness consequen
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13 INCIDENTAL TAKE STATEMENT Sectio
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Table 13.1 Summary of maximum annua
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in fewer larvae and juveniles, and
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Table 13.2 Estimated annual maximum
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1.2.1.8. Incidental Take Caused by
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characteristics of aquatic species,
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Table 13.5 Expected annual Environm
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Cause of Incidental Take Habitat Re
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Clear Lake, Gerber Reservoir, and T
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This term and condition is requirin
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13.4 Mandatory Monitoring and Repor
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Required hydrologic monitoring incl
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Table 13.7. Summary of LRS and SNS
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T&C or Mandatory Monitoring Mandato
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Table 13.9 Summary of reporting and
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Table 13.10 Summary of meetings req
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the above QA/QC procedures describe
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Barry, P.M., E.C. Janney, D.A. Hewi
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Burdick, S.M. and J. Rasmussen. 201
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Dunsmoor, L., L. Basdekas, B. Wood,
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Garen, D. 2011, Upper Klamath Basin
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Janney, E.C., B.S. Hayes, D.A. Hewi
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Laenen, A., and A.P. LeTourneau. 19
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Miller, R.R., and G.R. Smith. 1981.
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Perkins, D.L., and G.G. Scoppettone
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(Deltistes luxatus) in Tule and Cle
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Terwilliger, M. 2006. Physical habi
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USBR [U.S. Bureau of Reclamation].
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Williams, J.E. 2000. Chapter 13. Th
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Arthington, A.H., S.E. Bunn, N.L. P
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Beeman, J., S. Juhnke, G. Stutzer a
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Brommer, J.E. 2000. The evolution o
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Department of the Army Regional Gen
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Chilcote, M. W. 2003. Relationship
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Dunsmoor LK, and Huntington CW. 200
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Foott, J.S., R. Stone, E. Wiseman,
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Habera, J.W., R.J. Strange, B.D. Ca
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Hemstreet, T. 2013. Electronic mail
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Jordan, M. S. 2012. Hydraulic predi
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Kostow, K. E., A. R. Marshall and S
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MacFarlane, R. B., S. Hayes, and B.
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Moyle, P. B. 2002. Inland Fishes of
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PacifiCorp Klamath Hydroelectric Pr
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Oregon Department of Environmental
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Puckridge, J. T., F. Sheldon, K. F.
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Ring, T.E. and B. Watson. 1999. Eff
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Sommer, T. R., M. L. Nobriga, W. C.
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Taylor, R. 1991. A review of local
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USFWS [U. S. Fish and Wildlife Serv
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Ward G, and Armstrong N. 2010. Asse
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Winker, K., J. H. Rappole, and M. A
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77 FR 476. National Marine Fisherie
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UKL Elevation (feet) Active Storage
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16.2 Appendix B: Elevation Flow Dat
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490
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Week of Water Year 1981 1982 1983 1
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Water Year October November Decembe
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16.3 Appendix C: Description of Res
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4. Removal of Small Dams (permanent
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Information regarding consideration
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9. Piping Ditches a. Project Descri
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. Site-Specific Restrictions Restri
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6. Protection Measures The followin
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to enter or be placed where they co
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shall be distributed throughout the
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weed free straw, silt fences) are i
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the project is located, and compris
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2. Post Construction Monitoring and
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Median Seasonal Flow (acre-feet) Me
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Median Seasonal Net Inflow (acre-fe
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16.5 Appendix E: Observed and Model
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Observed and modeled proposed actio
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Observed and modeled proposed actio
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16.6 Appendix F: Analyzing the rela
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Table 1. Paired comparison of the c
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Table 3. The difference in the mean
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