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Susitna-Watana Hydroelectric Project Document
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Title:
Small mammal species composition and habitat use study, Study plan
Section 10.12 : Final study plan SuWa 200
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Alaska Energy Authority
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Final study plan
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Series (ARLIS-assigned report number):
Susitna-Watana Hydroelectric Project document number 200
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[Anchorage : Alaska Energy Authority, 2013]
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July 2013
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Study plan Section 10.12
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9 p.
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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)
Small Mammal Species Composition and
Habitat Use Study
Study Plan Section 10.12
Final Study Plan
Alaska Energy Authority
July 2013
FINAL STUDY PLAN SMALL MAMMAL SPECIES COMPOSITION AND HABITAT USE STUDY 10.12
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FERC Project No. 14241 Page 10.12-1 July 2013
10.12. Small Mammal Species Composition and Habitat Use
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). Section 10.12 of the RSP described the Small Mammal
Species Composition and Habitat Use Study. The study will be an office-based analysis to
review and synthesize available information on the occurrence and relative abundance of small
mammals in the Project area. The study will describe the species of small mammals known to
occur in the Project area and their patterns of habitat use. RSP 10.12 provided goals, objectives,
and proposed methods for data collection regarding small mammals.
On February 1, 2013, FERC staff issued its study plan determination (February 1 SPD) for 44 of
the 58 studies, approving 31 studies as filed and 13 with modifications. RSP Section 10.12 was
one of the 31 studies approved with no modifications. As such, in finalizing and issuing Final
Study Plan Section 10.12, AEA has made no modifications to this study from its Revised Study
Plan.
10.12.1. General Description of the Proposed Study
The Small Mammal Study will be an office-based analysis to review and synthesize available
information on the occurrence and relative abundance of small mammals in the Project area. The
study will describe the species of small mammals known to occur in the Project area and their
patterns of habitat use. Other small mammals, including snowshoe hares (Section 10.10) and bats
(Section 10.13), are addressed in other study plans.
Study Goal and Objectives
The goal of the Small Mammal Study is to synthesize baseline data on small mammals in the
Project area to enable habitat-based assessments of the impacts expected to occur from
development of the Project.
The Small Mammal Study has two specific objectives:
Describe the species composition and relative abundance of small mammals in the
Project area.
Describe the habitat associations of small mammals within the Project area.
10.12.2. Existing Information and Need for Additional Information
Small mammal species in the Susitna River basin include porcupine, hoary marmot, arctic
ground squirrel, red squirrel, collared pika, and several species each of voles, mice, and shrews
(ABR 2011). Species composition, relative abundance, and habitat use by small mammals were
studied intensively for the Alaska Power Authority (APA) Susitna Hydroelectric Project in 1980
and 1981 along 49 trapline transects (using both snap-traps and pitfall traps) located in a variety
of habitat types in the middle and upper Susitna River basin (Kessel et al. 1982). The APA
Susitna Hydroelectric Project study area for small mammals extended from Sherman (near Gold
Creek) on the west to the mouth of the Maclaren River on the east and within approximately 16
kilometers (10 miles) on each side of the Susitna River (Kessel et al. 1982).
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Since completion of the APA Susitna Hydroelectric Project studies in the 1980s, a new species
of small mammal—the Alaska tiny shrew (Sorex yukonicus)—was recognized and described by
Dokuchaev (1997) on the basis of morphological characteristics. The earliest specimen known
was trapped in 1982 near the upper Susitna River during the APA Susitna Hydroelectric Project
study. By 2007, the total number collected statewide had increased to 38 specimens from at least
22 widely separated locations (MacDonald and Cook 2009), indicating the species was much
more widespread than originally thought, occurring in low densities. Early information indicated
that it occurred primarily in riparian habitats, but it was also captured in scrub habitats as
trapping efforts expanded. The Alaska Natural Heritage Program classified the Alaska tiny shrew
as “unrankable” globally (GU), presumably because little information was available, and as
“vulnerable” in the state (S3; AKNHP 2011), presumably due to its restricted range and
relatively few populations known in North America. The species was included on the Bureau of
Land Management’s (BLM’s) Alaska list of sensitive species (2010). Based on more recent
genetic analyses, however, Hope et al. (2010) concluded that S. yukonicus is synonymous with
the Eurasian least shrew, S. minutissimus, and simply constitutes the eastern population of that
species, which occurs in Siberia and farther west in Eurasia. Hence, the classification and name
are likely to be revised in future taxonomic checklists.
No recent reports on small mammal studies in the middle or upper Susitna basin are available,
but additional information is available from other studies in surrounding regions, including
species inventories in Denali National Park and Preserve (Cook and MacDonald 2003) and on
Fort Richardson near Anchorage (Peirce 2003), and long-term population monitoring (1992–
2005) of three species of voles conducted in Denali National Park and Preserve by Rexstad and
Debevec (2006).
The APA Susitna Hydroelectric Project studies provided a thorough sampling of the small
mammal populations in the Project area. Although 30 years have elapsed since those studies, it is
unlikely that species distributions or habitat-use patterns have changed significantly in the
interim. Because of the often cyclical population fluctuations of small mammals and the lack of
effective mitigation to offset population losses in the impoundment zone, the wildlife data gap
analysis report (ABR 2011) questioned whether additional studies were warranted for the
Project. Hence, after further consideration of the likely results of the field sampling described
earlier in the Proposed Study Plan, and further consultation with the Alaska Department of Fish
and Game and the federal Bureau of Land Management, AEA has revised this study to focus on
reviewing and synthesizing all available information rather than conducting more field sampling
in 2013. In view of the intensive field sampling in the 1980s by the University of Alaska
Museum (Kessel et al. 1982) and its suitability for analysis by the Evaluation of Wildlife Habitat
Use (Section 10.19), this study will provide useful information for evaluating the direct effects of
habitat loss on small mammals as a result of Project development.
10.12.3. Study Area
The area of analysis for this study will consist of the entire Project area (Figure 10.12-1).
Existing data on the abundance and habitat associations of small mammals from the original
study for the APA Susitna Hydroelectric Project (Kessel et al. 1982) will be supplemented with
more recent data from other regional studies and will be applied to the wildlife habitat types
mapped throughout the reservoir inundation zone, associated facilities areas, and the access road
and power transmission corridors.
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10.12.4. Study Methods
This study will review, compile, and synthesize data on the occurrence and relative abundance of
the small mammal species captured and analyzed by Kessel et al. (1982). That information will
be supplemented with data from other small mammal trapping studies conducted recently in
Southcentral and Interior Alaska (including, but not limited to, Cook and MacDonald 2003,
Peirce 2003, Rexstad and Debevec 2006, MacDonald and Cook 2009, and specimen records
maintained by the University of Alaska Museum of the North in Fairbanks and the Alaska
Natural Heritage Program in Anchorage).
This information synthesis will then be applied to the wildlife habitat types mapped by the
Vegetation and Wildlife Habitat Mapping Study in the Upper and Middle Susitna Basin (Section
11.5) and will be included in the ranking of habitat values that will be the principal analytical
product of the Evaluation of Wildlife Habitat Use (Section 10.19). Kessel et al. (1982) quantified
habitat components and conducted detailed analyses of the abundance of small mammals in
relation to those habitat components. Standard trapping and survey methods for small mammals
(e.g., Jones et al. 1996) were used in that study, providing effective sampling of voles, lemmings,
and shrews by using both pitfall traps and snap-traps. Trapping data included the abundance of
species captured among different habitats types, which will be incorporated into the Evaluation
of Wildlife Habitat Use (Section 10.19) using a Geographical information System (GIS).
Additional information on small mammals will be collected as part of the study of Terrestrial
Furbearer Abundance and Habitat Use (described in detail in Section 10.10), which began in
August 2012 and will continue in August 2013 and 2014. In that study, t he abundance of voles
will be estimated by using live-trapping and mark–recapture methods in study plots located in
spruce forest and grassy meadow habitats. Captured voles will be weighed, ear-tagged, identified
to species and sex, and released. The proportion of tagged individuals to unmarked individuals
will be used to calculate an estimate of population abundance. In addition, a population index for
snowshoe hares will be estimated using counts of fecal pellets along transects located in selected
forest and shrub habitats.
10.12.5. Consistency with Generally Accepted Scientific Practice
The Small Mammal Study will rely on data that were collected using standard trapping
techniques (Jones et al. 1996). Analysis of habitat availability and use allows an ecosystem
approach to impact assessment, and GIS-based analysis has become a standard, straightforward
method of evaluating the impacts of habitat loss and alteration.
10.12.6. Schedule
As is depicted in Table 10.12-1, the review and synthesis of small mammal trapping data will be
conducted primarily in 2013, with analytical updates occurring in 2014 after further collection of
field data on vole and hare abundance and further refinement of the wildlife habitat map for the
Project. Initial and Updated Study Reports will be issued in February 2014 and 2015,
respectively. Study progress will be presented at Technical Workgroup meetings, which will be
held quarterly during 2013 and 2014.
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10.12.7. Relationship with Other Studies
As depicted in Figure 10.12-2, the Small Mammal Study will use information from the
Vegetation and Wildlife Habitat Mapping Study in the Upper and Middle Susitna Basin (Section
11.5) and the study of Terrestrial Furbearer Abundance and Habitat Use (Section 10.10). The
habitat types delineated for the wildlife habitat map will be used in the review and synthesis of
small mammal data. The terrestrial furbearer study will contribute estimates of vole density and
snowshoe hare abundance in selected habitat types. Data on species distribution, habitat
associations, and the number of captures will be used to assess the relative abundance of small
mammal species among the habitat types mapped in the study area, which will be used in the
habitat rankings prepared by the Evaluation of Wildlife Habitat Use (Section 10.19).
Construction and operation of the proposed Project has the potential to result in direct and
indirect effects on small mammals, including the following:
Direct and indirect habitat loss and alteration.
Potential direct mortality due to vehicle strikes, exposure to contaminants, and attraction
to garbage and human activity.
Potential changes in mortality due to changes in the abundance or distribution of
predators.
Potential physical and/or behavioral blockage of movements due to reservoir water and
ice conditions.
Potential effects on predator species.
For small mammals, the primary impact of direct and indirect habitat loss and alteration could
occur in the reservoir inundation zone, associated facilities footprints, and access and
transmission corridors.
During the impact assessment that will be conducted in 2015 for the FERC License Application,
data on the distribution and relative abundance of and habitat use by small mammals in the study
area can be used to assess Project impacts on these populations through geospatial analysis and
evaluation of the responses of the study species to other similar projects, as documented in the
scientific literature. Small mammal populations could also be affected over a larger region if
regional predator abundance is altered by the Project, as will be analyzed in the impact
assessment using data from other Project studies (i.e., Distribution, Abundance, and Habitat Use
by Large Carnivores [Section 10.8]; Wolverine Distribution, Abundance, and Habitat Occupancy
[Section 10.9]; Terrestrial Furbearer Abundance and Habitat Use [Section 10.10]; Aquatic
Furbearer Abundance and Habitat Use [Section 10.11]; and Surveys of Eagles and Other Raptors
[Section 10.14]). Using GIS software, species presence/absence data or relative abundance data
recorded among different habitat types mapped in the Project area can provide spatially explicit
impact predictions. The direct and indirect impacts of the Project can be evaluated by overlaying
the reservoir, related infrastructure areas, and access road and power transmission corridors onto
the habitat map to evaluate direct impacts and indirect impacts on preferred habitats. The GIS
analysis can be combined with information from the literature to estimate the potential
geographic extent, frequency, duration, and magnitude of Project effects on small mammal
populations. Additional information collected for the various studies of predators can be used to
evaluate the potential area over which small mammal populations may be affected by changes in
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predation rates. The results of these analyses to assess Project impacts can be used to evaluate
protection, mitigation, and enhancement (PM&E) measures, as appropriate.
10.12.8. Level of Effort and Cost
Most of the review and synthesis effort will occur in the first year (2013) and will be available
for the Initial Study Report, but revisions will be necessary to include additional data collected
on vole and hare population indices in 2014 and to incorporate the revisions made for the final
wildlife habitat map in 2014 for the Updated Study Report. Total study costs are estimated to be
approximately $50,000 over both years.
10.12.9. Literature Cited
ABR. 2011. Wildlife data-gap analysis for the proposed Susitna–Watana Hydroelectric Project.
Draft report, August 16, 2011, prepared for the Alaska Energy Authority by ABR, Inc.—
Environmental Research & Services, Fairbanks, Alaska. 114 pp.
AKNHP (Alaska Natural Heritage Program). 2011. Species tracking list (updated January 2011).
Alaska Natural Heritage Program, University of Alaska, Anchorage. 31 pp. Available
online (accessed August 12, 2011): http://aknhp.uaa.alaska.edu/wp-content/uploads/
2010/11/All_Tracking_Lists_Combined1.pdf.
BLM (Bureau of Land Management). 2010. BLM–Alaska sensitive animal and plant lists.
Alaska State Office, Anchorage.
Cook, J. A., and S. O. MacDonald. 2003. Mammal inventory of Alaska’s national parks and
preserves: Denali National Park and Preserve. 2002 annual report for National Park
Service, Alaska Region Survey and Inventory Program, Anchorage, by Idaho State
University, Pocatello. 24 pp.
Dokuchaev, N. E. 1997. A new species of shrew (Soricidae, Insectivora) from Alaska. Journal of
Mammalogy 78: 811–817.
Hope, A. G., E. Waltari, N. E. Dokuchaev, S. Abramov, T. Dupal, A. Tsvetkova, H. Henttonen,
S. O. MacDonald, and J. A. Cook. 2010. High-latitude diversification within Eurasian
least shrews and Alaska tiny shrews (Soricidae). Journal of Mammalogy 91: 1041–1057.
Jones, C., W. J. McShea, M. J. Conroy, and T. H. Kunz. 1996. Capturing mammals. Pages 115–
155 in D. E. Wilson, F. R. Cole, J. D. Nichols, R. Rudran, and M. S. Foster, editors.
Measuring and Monitoring Biological Diversity: Standard Methods for Mammals.
Smithsonian Institution Press, Washington, D.C.
Kessel, B., S. O. MacDonald, D. D. Gibson, B. A. Cooper, and B. A. Anderson. 1982. Susitna
Hydroelectric Project environmental studies, Phase I final report—Subtask 7.11: Birds
and non-game mammals. Report by University of Alaska Museum, Fairbanks, and
Terrestrial Environmental Specialists, Inc., Phoenix, NY for Alaska Power Authority,
Anchorage. 149 pp.
MacDonald, S. O., and J. A. Cook. 2009. Recent Mammals of Alaska. University of Alaska
Press, Fairbanks. 387 pp.
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Peirce, K. N. 2003. A small mammal inventory on Fort Richardson, Alaska. Report by Center for
Environmental Management of Military Lands, Colorado State University, for U.S. Army
Environmental Resources Department, Fort Richardson, Alaska. 40 pp.
Rexstad, E., and E. Debevec. 2006. Dynamics of small mammal populations in the Rock Creek
watershed, Denali National Park and Preserve. Alaska Park Science 6: 69–72. Available
online (accessed August 10, 2011): http://www.nps.gov/akso/AKParkScience/
symposium2006/rexstad.pdf.
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10.12.10. Tables
Table 10.12-1. Schedule for implementation of the Small Mammal Study.
Activity
2013 2014 2015
1 Q 2 Q 3 Q 4 Q 1 Q 2 Q 3 Q 4 Q 1 Q
Review & synthesize results of regional
studies of small mammals
Apply results of review & synthesis to
available wildlife habitat mapping
Incorporate results from other studies
(snowshoe hare & vole density estimates,
wildlife habitat mapping updates)
Initial Study Report Δ
Updated Study Report ▲
Legend:
Planned Activity
Follow-up activity (as needed)
Δ Initial Study Report
▲ Updated Study Report
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10.12.11. Figures
Figure 10.12-1. Study area for the small mammals study.
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Terrestrial Furbearer
Abundance & Habitat Use
(Section 10.10)
Vegetation & Wildlife Habitat
Mapping Study in the Upper
& Middle Susitna Basin
(Section 11.5)
Preliminary wildlife habitat
map & descriptions of habitat
types (2Q–2013 & 2Q–2014)
Snowshoe hare & vole
density estimates in
selected habitat types (3Q–
2012, 3Q–2013, 3Q–2014)
STUDY INTERDEPENDENCIES FOR SMALL MAMMAL STUDY
Review and
synthesis of regional
studies of small
mammals
Evaluation of Wildlife Habitat
Use (Section 10.19)
Occurrence & relative
abundance of species among
habitat types (3Q–2013 &
3Q–2014)
Figure 10.12-2. Study interdependencies for the small mammal study .