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Susitna-Watana Hydroelectric Project Document
ARLIS Uniform Cover Page
Title:
The future Watana reservoir fish community and risk of entrainment study,
Study plan Section 9.10 : Final study plan SuWa 200
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Alaska Energy Authority
AEA-identified category, if specified:
Final study plan
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Series (ARLIS-assigned report number):
Susitna-Watana Hydroelectric Project document number 200
Existing numbers on document:
Published by:
[Anchorage : Alaska Energy Authority, 2013]
Date published:
July 2013
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Date or date range of report:
Volume and/or Part numbers:
Study plan Section 9.10
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Pagination:
14 p.
Related work(s):
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Notes:
All reports in the Susitna-Watana Hydroelectric Project Document series include an ARLIS-
produced cover page and an ARLIS-assigned number for uniformity and citability. All reports
are posted online at http://www.arlis.org/resources/susitna-watana/
Susitna-Watana Hydroelectric Project
(FERC No. 14241)
The Future Watana Reservoir Fish Community and
Risk of Entrainment Study
Study Plan Section 9.10
Final Study Plan
Alaska Energy Authority
July 2013
FINAL STUDY PLAN THE FUTURE WATANA RESERVOIR FISH COMMUNITY
AND RISK OF ENTRAINMENT STUDY 9.10
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FERC Project No. 14241 Page 9.10-1 July 2013
9.10. The Future Watana Reservoir Fish Community and Risk of
Entrainment Study
On December 14, 2012, Alaska Energy Authority (AEA) filed with the Federal Energy
Regulatory Commission (FERC or Commission) its Revised Study Plan (RSP), which included
58 individual study plans (AEA 2012). Included within the RSP was The Future Watana
Reservoir Fish Community and Risk of Entrainment Study, Section 9.10. RSP Section 9.10
focuses on understanding the relationship between Project design, operations, lacustrine habitat,
and the potential fish community in the proposed Watana Reservoir is important for assessing
potential Project impacts.
On February 1, 2013, FERC staff issued its study determination (February 1 SPD) for 44 of the
58 studies, approving 31 studies as filed and 13 with modifications. RSP Section 9.10 was one
of the 13 approved with modifications. In its February 1 SPD, FERC recommended the
following:
We recommend modifying AEA’s proposed evaluation of the potential to establish viable
populations of anadromous salmonids upstream of the project, specified in task 4 of section
9.10.4.2, to include evaluation of the production potential for Chinook, sockeye, chum, and coho
salmon in reservoir and riverine habitats upstream of the dam.
In accordance to FERC’s February 1 SPD, AEA has included this modification in the Final
Study Plan.
9.10.1. General Description of the Proposed Study
The nature of the fish community inhabiting the proposed Watana Reservoir will depend on a
suite of interrelated factors affecting fish populations and their habitat. These factors may be
influenced by the design and operation of the Project. This study plan describes the efforts that
will be implemented to predict the fish community that will develop in the Project’s reservoir
and identify the effects of the Project on the future reservoir fish community. Figure 9.10-2
shows the relationship between this study and other study programs.
Study Goals and Objectives
Construction and operation of the Project will result in inundation of the river upstream from the
dam. Several operational scenarios will also be considered as part of the licensing studies. Some
operating scenarios, such as load-following, could result in relatively large and frequent
fluctuations of the reservoir water surface elevation. Operations would result in seasonal
differences in pool elevation such as a winter or early-springtime drawdown in advance of the
annual melt of accumulated snow during early summer.
Construction of the Project will fundamentally change the fish habitat characteristics in the area
to be inundated. About 39 miles of mainstem river plus several miles of tributary stream will be
converted to lacustrine habitat. Conversion from riverine habitat to lacustrine habitat will be
beneficial for some fish species and detrimental to others, resulting in a modified fish
community. Depending upon the fish protection measures included in the Project license and
specific engineering design elements, the modified fish community may be subject to
entrainment and mortality as a result of spill or passage through turbines. This study will
provide information and tools needed for predicting the likely changes to the fish community due
FINAL STUDY PLAN THE FUTURE WATANA RESERVOIR FISH COMMUNITY
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to habitat conversion, potential mortality from entrainment, and for assessing the potential
Project operational effects on lacustrine habitat following Project construction.
Understanding the relationship between Project design, operations, lacustrine habitat, and the
potential fish community in the proposed Watana Reservoir is important for assessing potential
Project impacts. The proposed Watana Reservoir has the potential to provide public benefits in
the form of recreational fishing opportunities as well development of commercial or subsistence
fisheries. Identifying the potential fish community and species with commercial, subsistence,
and sportfish values is also important for identifying alternative fishery management strategies in
advance of Project construction.
The overarching goal of this study is to predict the fish community that will develop in the
Project reservoir based on the existing species and the habitat that will be created in the
inundation zone, and to characterize the potential loss from entrainment.
Specific objectives include the following:
1. Develop scenarios for anticipated daily and seasonal changes in reservoir habitat
characteristics based on predicted reservoir operations, size, temperatures, and water
quality and depth profiles.
2. Develop scenarios for future reservoir fish communities based on current fish species
composition upstream of the proposed dam site and enhancement potential for select
salmon species incorporating anticipated daily and seasonal changes in reservoir habitat
characteristics.
3. Characterize potential management options including recreational, commercial, and
subsistence uses of the reservoir fishery.
4. Conduct a qualitative desktop analysis on the potential for entrainment of fish species
inhabiting the proposed reservoir upstream of Watana Dam.
9.10.2. Existing Information and Need for Additional Information
Information regarding resident species, non-salmon anadromous species, and the freshwater
rearing life stages of anadromous salmon was collected as part of the studies conducted during
the early 1980s. Existing information includes the spatial and temporal distribution of fish
species and their relative abundance. The Aquatic Resources Data Gap Analysis (ARDGA;
AEA 2011a) and Pre-Application Document (PAD) (AEA 2011b) summarize this existing
information and also identify data gaps for resident and rearing anadromous fish.
At least eight species of fish are known to occur in the Upper Susitna River (AEA 2011a). These
species are Arctic grayling, Dolly Varden, humpback whitefish (Coregonus spp.), round
whitefish, burbot, longnose sucker, Chinook salmon, and sculpin (all assumed to be slimy
sculpin). Northern pike, Alaska blackfish, and lake trout may also be present. Chinook salmon
are the only anadromous species documented in the Upper Susitna River.
In the proposed impoundment zone, Arctic grayling are believed to be the most abundant fish
species (AEA 2011a) and were found to spawn in tributary pools. In tributaries, juvenile
grayling were found in side channels, side sloughs, and pool margins and in the mainstem at
tributary mouths and clear water sloughs during early summer (AEA 2011b). Dolly Varden
populations in the Upper Susitna River are apparently small but widely distributed (AEA 2011b).
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Burbot in the Upper Susitna River were documented in mainstem habitats with backwater eddies
and gravel substrate. Longnose suckers were less abundant in the Upper Susitna River than
downstream of Devils Canyon (river mile [RM] 150). Lake trout were documented in lakes near
the proposed impoundment zone but the impoundment zone has not yet been sampled.
In the 1980s, the Alaska Department of Fish and Game (ADF&G) completed an investigation of
feasibility of upstream salmon passage through Devils Canyon and the enhancement potential in
the river basin upstream of Devils Canyon (Barrick et al. 1983). Information from this historic
study will be used in combination with data collected in 2013 and workgroup meetings with
ADF&G management biologists to characterize the potential future reservoir fish community.
This study is needed to provide information and tools needed for predicting the likely changes to
the fish community due to habitat conversion, for determining potential mortality from
entrainment, and for assessing the potential Project operational effects on lacustrine habitat
following Project construction.
9.10.3. Study Area
The study area (Figure 9.10-1) encompasses all portions of the basin to be inundated by the
proposed Watana Reservoir up to the maximum reservoir water surface elevation to be
determined during finalization of design and operational scenarios. About 39 miles of mainstem
river (beginning at the dam site at RM 184), plus an unknown amount of tributary stream, will be
converted to lacustrine habitat. During normal operation, the reservoir level may fluctuate
substantially on a daily and seasonal basis. Annual drawdowns are anticipated to exceed 100
feet with a maximum drawdown of 150 feet. The Project is currently planned to be operated in a
load-following mode to maximize firm power generation during winter (November through
April), but inflows into the reservoir during this period are anticipated to be relatively low.
9.10.4. Study Methods
The following sections describe the approach that will be used to address each of the four
interrelated study objectives associated with the Future Watana Reservoir Fish Community and
Risk of Entrainment Study. Each component incorporates significant agency recommendations
regarding the general study approach and specific methods to be used. These were developed
collaboratively during the drafting of the relevant study request. Where appropriate, each study
component has been broken down into separate tasks.
9.10.4.1. Reservoir Habitat Scenarios
Based on the alternative Project operating scenarios identified by Project engineers, this study
component will develop corresponding scenarios for anticipated daily and seasonal changes in
reservoir habitat characteristics. This study component is composed of the three following tasks
that will consider reservoir conditions related to the relative size of lacustrine zones, water
temperature, and turbidity.
Task 1 – Lacustrine Zone Estimation
Project operations will influence the relative size of different lacustrine zones and, as a result, the
amount of habitat for aquatic biota that inhabit each zone. This task will coordinate with the
operations modeling study team to adapt an existing model, such as HEC-ResSim, or develop a
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new unsteady flow hydraulic model of the proposed reservoir that can be used to evaluate daily
and seasonal changes in reservoir depth and the amount of exposed shoreline. Based on Light
Detection and Ranging (LiDAR) data and a series of transects across the proposed reservoir,
model results will provide reservoir water surface elevations and depths that will be used to
develop estimates of the size of each of the following lacustrine zones under the alternative
operating scenarios identified in coordination with project engineers:
Varial Zone: Area alternately wetted and dewatered by water level fluctuations; can
include some or all of the littoral zone.
Littoral Zone: Near-shore area extending to the deepest extent of light penetration
sufficient for primary production.
Limnetic Zone: Open-water layer with sufficient light penetration for primary production
to occur.
Profundal Zone: Open-water layer too deep for primary production to occur; below the
limnetic zone.
Benthic Zone: Bottom layer of the reservoir associated with the substrate and underlying
all other zones.
An important part of this task will be the development of assumptions related to reservoir
operations to be incorporated into the hydraulic model. These model assumptions will be
developed collaboratively with the Fish and Aquatic Technical Workgroup (TWG). Additional
assumptions pertain to how the lacustrine zone is defined temporally and spatially. Temporal
aspects of the defined lacustrine zone will consider minimum and maximum time intervals
appropriate to the frequency and magnitude of water level fluctuations expected under the
alternative operating scenarios, in particular those related to peaking operations. Spatial
definitions will consider turbidity or other factors related to light penetration that also may vary
at least seasonally.
Task 2 – Water Temperature Modeling
This task will involve the development of a water temperature model of the proposed reservoir
that can be used to evaluate daily and seasonal changes in water temperatures and the potential
for thermal stratification. The water temperature model will be developed in coordination with
the water quality assessment team and as part of the proposed Water Quality Modeling Study. It
is anticipated that the Environmental Fluid Dynamics Code (EFDC), will be used for this effort
based on the review of available models described in Water Quality Monitoring Study (Section
5.6). Model results will be used to predict daily and seasonal variations in reservoir
temperatures, including temperature profiles, and identify the potential for thermal stratification.
This task will summarize the reservoir temperature model results including an assessment of how
the results relate to the future reservoir fish community. Details regarding the implementation of
the water quality model are described in Section 5.6 though specific outputs necessary for this
study component will be developed through an iterative and collaborative process with the water
quality study team. Completion of the initial study report for the Water Quality Modeling Study
is expected in the first quarter of 2014. However, model outputs related to reservoir temperature
will be obtained as they become available.
Task 3 – Reservoir Turbidity
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Turbidity levels can influence the suitability of aquatic habitat for certain fish species. This task
will involve reviewing available information to identify turbidity thresholds that can limit
reservoir habitat utilization for species that may otherwise overwinter in the Watana Reservoir.
The target species for this effort are lake trout, burbot, grayling, and whitefish. Historic
information collected in the Susitna basin during the 1980s and synthesized as part of a 2012
study (Synthesis of Exiting Fish Population Data) will be reviewed to identify utilization relative
to turbidity levels. Information collected in 2012 as part of the Upper Susitna River Fish
Distribution and Habitat Study will also be reviewed as well as turbidity threshold information
available for the target species from other out-of-basin literature sources. This information will
be compared to turbidity levels expected to occur in the Watana Reservoir that are identified in
coordination with the water quality assessment team. Species-specific turbidity exceedances in
the Watana Reservoir during winter will be identified to predict the degree, if any, to which
turbidity will limit the overwintering use of reservoir habitat by lake trout, burbot, grayling, and
whitefish.
9.10.4.2. Reservoir Fish Community Scenarios
Creation of the reservoir and operation of the Project will drastically alter the habitat available to
the existing fish community in the inundation zone. The future reservoir fish community will be
determined by the altered habitat conditions, as well as the segment of the existing fish
community expected to utilize the reservoir. This study component will develop scenarios for
future reservoir fish communities based on the current fish species composition upstream of the
proposed dam site, anticipated reservoir habitat characteristics, and management practices
acceptable to ADF&G. This study component is composed of the following four tasks related to
the existing fish community, potential use of the reservoir by these species, and the potential
presences of invasive species.
Task 1 – Define Existing Fish Community
Species that comprise the existing fish community in the Susitna River and certain subbasins
represent the source stocks from which the reservoir could be colonized. In this task,
information from two studies conducted during 2012, the Synthesis of Existing Fish Population
Data Study and the Upper Susitna River Fish Distribution and Habitat Study, will be reviewed to
characterize the existing fish community in the mainstem river and any tributaries or lakes that
could colonize the reservoir. Potential colonizing species will be identified based on their
presence in the inundation zone, proximity/connectivity to the inundation zone, and the
likelihood of potential movements to the inundation zone.
Task 2 – Identify Potential Use of Lacustrine Habitat
Although the reservoir could be colonized by fish species identified in Task 1, future reservoir
habitat may not be suitable for all species. This task will involve a literature review to identify
species in the existing fish community that may use lacustrine habitat for one or more life history
stages. In the absence of such information, general utilization of lacustrine habitat in other
systems will be reviewed. A white paper will be prepared that identifies the life history and
habitat requirements for each species, with a focus on lacustrine elements. The white paper will
be drafted during 2Q and 3Q, 2013 and findings will be incorporated into the Initial Study
Report and the Updated Study Report. The discussion for each species will include an
assessment of uncertainty in predicting their lacustrine habitat use. This assessment will be
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written to aid in the development of a post-construction monitoring program by identifying such
uncertainties as expected life histories or those related to future reservoir habitat conditions.
Task 3 – Identify Potential Invasive Species
Northern pike are considered an invasive species in the Susitna drainage and have spread
throughout the system from the Yenta drainage after being illegally introduced in the 1950s
(AEA 2011b). Alaska blackfish are also considered an invasive species and, while not captured
in the Susitna River, may have been introduced to the system. This task will identify the
presence of invasive species in lakes and ponds that are currently disconnected from the
mainstem but have the potential to be inundated. Information from the two 2012 studies
identified above will be reviewed to identify water bodies in which invasive species have been
found and that have the potential to be inundated.
Task 4 – Identify Potential for Anadromous versus Land-Locked Salmon-Based
Community
This task summarizes the potential to establish viable populations of anadromous salmon
upstream of the proposed Project and the potential to affect native fish communities. This task
will also evaluate the production potential for Chinook, sockeye, chum, and coho salmon in
reservoir and riverine habitats upstream of the dam. The evaluation of production potential
upstream of the Project will be based on the 1983 study by ADF&G (Barrick et al 1983).
Depending on fish passage considerations, an alternative land-locked salmonid community will
also be assessed. Potential effects of these species on native fish communities will be addressed.
A literature review will focus on habitat utilization by relevant species in newly created
reservoirs where such information is available. This effort will be conducted during 2Q and 3Q
2013 and findings will be synthesized to comprise relevant sections of the Initial Study Report
and Updated Study Report.
9.10.4.3. Reservoir Fishery Management Options
This study component will characterize potential management options for a future reservoir
fishery. A future fishery in the Watana Reservoir will be dependent upon the habitat conditions
and fish community expected to occur in the reservoir, as described by the previous study
components. Management options related to a reservoir fishery will be dependent on public
access and recreational goals established for the reservoir and consistency with ADF&G
management actions, as well as fish passage As such, analyses associated with this study
component will be conducted in 2014 when more information on public access and recreational
goals for the reservoir are available. Implementation of this study component will involve
collaborating with ADF&G in the development of alternative recreational, commercial, and
subsistence fishery management strategies for the reservoir. This effort will also coordinate with
the recreation team to determine the recreational basis and potential access in support of a
potential fishery. The technical memorandum for the overall study will include a section in
which the potential management options for a future reservoir fishery, developed in collaboration
with ADF&G and in coordination with the recreation team, are described in detail.
9.10.4.4. Entrainment Analysis
Fish inhabiting the proposed reservoir could be susceptible to entrainment through the Project
(turbines or spillways) or impingement on the intake trash racks. This study component will
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involve conducting a desktop analysis of the potential for entrainment and impingement of fish
species inhabiting the proposed Watana Reservoir. This study component is comprised of the
following three tasks related to identifying Project design and operating scenarios, reviewing
relevant literature related to entrainment at other projects and biological information for target
species, and analyzing this information to assess entrainment and impingement risks at the
Project. Fish passage provisions, and the presence of anadromous fish, have implications
regarding the overall number of species and individuals to be considered in evaluating potential
entrainment or impingement risks; thus, the selection of target species for entrainment will be
drawn from the reservoir fish community scenerios and identified in collaboration with the Fish
and Aquatic TWG. The work product for this study component will be a technical memorandum
summarizing the entrainment analysis that will entail the following tasks.
Task 1 – Identify Project Design/Operating Scenarios
Potential entrainment risks are influenced by Project design and operations. This task will
involve coordinating with Project engineers to understand alternative Project designs and
operating scenarios. This task is anticipated to be conducted in 2014 when more dam design and
operational details are available. Specific design and operational details to be considered that
can directly influence entrainment risks include the following:
• Intake approach velocities
• Trash rack spacing
• Intake depths and design
• Outlet depths and design
• Operating head
• Turbine design
• Turbine speed
• Generation
• Spillway design
• Spill height
• Spill frequency
Task 2 – Literature Review
An abundance of information is available in the literature regarding fish entrainment at
hydropower projects (i.e., EPRI 1997; Franke et al. 1997; FERC 1995). This task will entail
reviewing such information as well as other analyses of entrainment risks with a focus on deep
water intakes and cold water reservoirs. Biological information related to the future Watana
Reservoir fish community identified as part of this study will also be considered to identify
species and life stages expected to inhabit the reservoir that may be at risk of entrainment or
impingement. Additional biological information related to entrainment and impingement risks
will be obtained from the literature. Such information includes the swimming ability of target
species, which will influence their ability to avoid entrainment as they approach the intakes, as
well as fish size (i.e., body length and width), which will influence impingement risks. General
behavioral information related to movements in the water column and reservoir habitat use will
also be reviewed.
Task 3 – Desktop Analysis
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This task will involve synthesizing the information collected in the previous tasks to conduct a
desktop analysis identifying the potential vulnerability of target species in the anticipated
reservoir community to entrainment and impingement mortality at the proposed dam under
alternative design and operating scenarios. Because the size and composition of fish populations
comprising the future reservoir community is theoretical under pre-Project conditions, rates of
entrainment or impingement will not be predicted as part of this task. Rather, this analysis will
focus on identifying species and life stages at risk of entrainment or impingement based on their
size, swimming ability, periodicity, and/or behavior. The analysis will also identify the relative
risks associated with different potential sources of indirect or direct mortality, including
impingement, strike, shear, grinding, turbulence, cavitation, pressure changes, and dissolved gas
levels.
9.10.4.5. Work Products
Deliverable work products include the following:
White Paper on Potential Use of Lacustrine Habitat
As described above, a white paper will be prepared that identifies the potential use of lacustrine
habitat. This work product will rely on existing information developed in 2012 as well as a
review of relevant literature. Because the contents of this work product do not require input
from water quality modeling or operational scenarios, it will be completed in 3Q, 2013.
Technical Memorandum on Entrainment Analysis
A technical memorandum will be prepared that summarizes the results of the entrainment
analysis, including a summary of relevant Project design/operational scenarios, a review of
available literature pertinent to entrainment/impingement risks of target species, and the methods
and results of the desktop entrainment analysis. Because this work product is dependent on input
regarding Project design and operating scenarios, it will be completed in 2Q, 2014.
Study Reports
Initial and Updated Study Reports that summarize study progress and results gathered to date
will be prepared and presented to resource agency personnel and other licensing participants,
along with spatial data products. These Study Reports will represent the primary work products
for this study and will provide detailed methods and findings associated with all of the
aforementioned tasks related to Reservoir Habitat Scenarios, Reservoir Fish Community
Scenarios, Reservoir Fishery Management Options, and the Entrainment Analysis. When
available, the Initial and /or Updated Study Reports will incorporate results provided in the white
paper on potential use of lacustrine habitat, and the technical memorandum related to the
entrainment analysis. Along with the study reports, spatial data products will be provided that
include shape files of the various lacustrine zones for each alternative operating scenario. All
map and spatial data products will be delivered in the two-dimensional Alaska Albers Conical
Equal Area projection, and North American Datum of 1983 (NAD 83) horizontal datum
consistent with Alaska Department of Natural Resources (ADNR) standards. Naming
conventions of files and data fields, spatial resolution, and metadata descriptions must meet the
ADNR standards established for the Project.
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9.10.5. Consistency with Generally Accepted Scientific Practice
The study methods have been developed in consultation with licensing participants. The
methods chosen to accomplish this effort are consistent with standard techniques used
throughout the fisheries scientific community. The use of models is a common technique used
for assessing potential effects of a proposed project. The proposed modeling frameworks
described below were developed by the U.S. Army Corps of Engineers and the U.S.
Environmental Protection Agency specifically for predicting the behavior of reservoirs and
simulating physical water resource processes.
9.10.6. Schedule
This is largely a desktop analysis that will be completed in late 2013 and 2014 as information
from other studies becomes available. The schedule for this study is shown in Table 9.10-1.
Results from the Reservoir Habitat Study component will inform the Reservoir Fish Community
Study component. In turn, results from the Reservoir Fish Community Study component will
inform both the Reservoir Fishery and Entrainment Study components. As such, the schedule
reflects the appropriate ordering of implementation for each study component. Initial and
Updated Study reports documenting actions taken to date will be issued within 1 and 2 years,
respectively, of FERC’s Study Plan Determination (i.e., February 1, 2013).
9.10.7. Relationship with Other Studies
The Future Watana Reservoir Fish Community and Risk of Entrainment Study is interrelated to
several AEA studies (Figure 9.10-2). The flow of information into and out of this study is
anticipated to occur over the two-year study period through an iterative process. As relevant data
(described above) is collected, it will be disseminated to other participants in the Fish Program
and Recreational Resources. To maximize communication among the Fish Study Program, study
leads will participate in regularly scheduled internal meetings where preliminary data will be
presented and implications to other studies discussed.
In addition to Project design and operations, five Project studies will interrelate by providing
input information useful to the Reservoir Fish Community and Entrainment Study. In the fourth
quarter of 2013, the Fish Passage Feasibility Study (Section 9.11.4) will provide input
information on concepts and alternatives as an iterative process that will inform the future fish
community. The Upper River Fish Distribution and Abundance Study (Section 9.5.4.3.1) will
provide information on the potential reservoir fish community in the 2013 and 2014 Study
Reports. The Fish Passage Feasibility Study (Section 9.11.4) will also provide information on
entrainment risk with preliminary engineering and design alternatives in the 2013 and 2014
Study Reports. The Water Quality Modeling Study (Section 5.6.4) will provide information in
the third and fourth quarters of 2014 on temperature and turbidity that will be used to assess
reservoir habitat. The Recreational Resources Study (Section 12.5) Initial Study Report will
provide information on how recreational use and demand of the reservoir may impact the fishery.
The Future Watana Reservoir Fish Community and Risk of Entrainment Study will also
interrelate with three other Project studies by providing useful output information (Figure 9.10-
2). The desktop analysis of potential entrainment will provide information on entainment risk to
the Fish Passage Feasibility Study (Section 9.11) in the second quarter of 2014 and output back
to the Watana Reservoir Fish Community Study (Section 9.10). Evaluating scenarios for
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reservoir habitat, fishery management options, and future reservoir fish communities in the first
quarter 2014 will inform the Future Watana Reservoir Fish Community Study (Section 9.10).
The reservoir fisheries component of the Reservoir Fish Community and Entrainment Study will
used to evaluate fishery management options in the second quarter of 2014 and used and inform
the Recreation Resources Study (Section 12.5).
9.10.8. Level of Effort and Cost
Several components of this study will rely on modeling or other efforts developed in
coordination with other study programs. As such, the level of effort and expected cost associated
with each study component is dependent upon the distribution of effort among the different study
programs. The total estimated cost for this study is $205,000. The estimated costs associated
with each study component are provided below and include assumptions related to the
distribution of effort. The staffing and costs for this study will be further refined as other related
portions of the 2013–2014 study program develop.
Reservoir Habitat Scenarios
The estimated cost to complete this study component is $60,000. This cost assumes that the
operations modeling study team will perform the majority of the reservoir hydraulic modeling
effort and water quality study team will perform the majority of the water temperature modeling
effort.
Reservoir Fish Community Scenarios
The estimated cost for this study component is $65,000.
Reservoir Fishery Management Options
The estimated cost for this study component is $40,000. This cost assumes that the recreation
study team will develop the recreational basis for a future reservoir fishery.
Entrainment Analysis
The estimated cost for this study component is $40,000.
9.10.9. Literature Cited
AEA (Alaska Energy Authority). 2011a. Aquatic Resources Gap Analysis. Prepared by HDR,
Inc., Anchorage. 107 pp.
AEA. 2011b. Pre-application Document: Susitna-Watana Hydroelectric Project, FERC Project
No. 14241. December 2011. Prepared for the Federal Energy Regulatory Commission,
Washington, D.C.
Barrick L., Kepshire, B., G Cunningham. 1983. Upper Susitna River Salmon Enhancement
Study. Alaska Department of Fish and Game FRED Report Number 4. 156 pp.
EPRI (Electric Power Research Institute). 1997. Turbine survival and entrainment database –
field tests. EPRI Report No. TR-108630. Prepared by Alden Research Laboratory, Inc.
Holden, MA. 13 pp and two 3.5-inch diskettes.
FINAL STUDY PLAN THE FUTURE WATANA RESERVOIR FISH COMMUNITY
AND RISK OF ENTRAINMENT STUDY 9.10
Susitna-Watana Hydroelectric Project Alaska Energy Authority
FERC Project No. 14241 Page 9.10-11 July 2013
FERC (Federal Energy Regulatory Commission). 1995. Preliminary assessment of fish
entrainment at hydropower projects – volume 1 (Paper No. DPR-10). Office of
Hydropower Licensing, FERC, Washington, D.C.
Franke, G.F., D.R. Webb, R.K. Fisher, D. Mathur, P.N. Hopping, P.A. March, M.R. Headrick,
I.T. Laczo, Y. Ventikos, F. Sotiropoulus. 1997. Development of environmentally
advanced hydropower turbine system design concepts. U.S. Dept. of Energy and
Hydropower Research Foundation. July 1997.
FINAL STUDY PLAN THE FUTURE WATANA RESERVOIR FISH COMMUNITY
AND RISK OF ENTRAINMENT STUDY 9.10
Susitna-Watana Hydroelectric Project Alaska Energy Authority
FERC Project No. 14241 Page 9.10-12 July 2013
9.10.10. Tables
Table 9.10-1. Schedule for implementation of the Future Watana Reservoir Fish Community and Risk of Entrainment
Study.
Activity 2013 2014 2015
1 Q 2 Q 3 Q 4 Q 1 Q 2 Q 3 Q 4 Q 1 Q
Reservoir Habitat Scenarios -------
-
Initial Study Report Δ
Reservoir Fish Community Scenarios
Reservoir Fishery Management Options
Entrainment Analysis
Updated Study Report ▲
Legend:
Planned Activity
----- Follow-up activity (as needed)
Δ Initial Study Report
▲ Updated Study Report
FINAL STUDY PLAN THE FUTURE WATANA RESERVOIR FISH COMMUNITY AND RISK OF ENTRAINMENT STUDY 9.10
Susitna-Watana Hydroelectric Project Alaska Energy Authority
FERC Project No. 14241 Page 13 July 2013
9.10.11. Figures
Figure 9.10-1. Map of study area for Future Watana Reservoir Fish Community and Risk of Entrainment Study.
FINAL STUDY PLAN THE FUTURE WATANA RESERVOIR FISH COMMUNITY AND RISK OF ENTRAINMENT STUDY 9.10
Susitna-Watana Hydroelectric Project Alaska Energy Authority
FERC Project No. 14241 Page 14 July 2013
Figure 9.10-2. Flow chart showing relationships between components of the Future Watana Reservoir Fish Community and Risk of Entrainment Study (ovals), other
study programs, and related information.