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Susitna-Watana Hydroelectric Project Document
ARLIS Uniform Cover Page
Title:
SuWa 258
Initial Study Report Meetings, October 21, 2014 : Alaska Energy Authority -
Board Room, 813 West Northern Lights Blvd., Anchorage, Alaska 99503
Author(s) – Personal:
Author(s) – Corporate:
Initial Study Report Meetings (2014 October 21 : Anchorage, Alaska)
Of the twenty presentations, fifteen had been prepared by ABR Inc., Environmental Research and
Services and six by Alaska Department of Fish and Game (some jointly).
AEA-identified category, if specified:
November 14, 2014 technical memorandum filings
AEA-identified series, if specified:
Series (ARLIS-assigned report number): Existing numbers on document:
Susitna-Watana Hydroelectric Project document number 258
Published by: Date published:
[Anchorage, Alaska : Alaska Energy Authority, 2014] November 15, 2014
Published for: Date or date range of report:
Volume and/or Part numbers:
Final or Draft status, as indicated:
Attachment D
Document type: Pagination:
Technical memorandum 562 p. in various pagings
Related work(s): Pages added/changed by ARLIS:
Cover letter to this report: Susitna-Watana Hydroelectric
Project, FERC Project no. 14241-000; Filing of Initial Study Plan
Meetings transcripts and additional information in response to
October 2014 Initial Study Plan Meetings. (SuWa 254)
Attachments A-C (SuWa 255-257) and E-N (SuWa 259-268)
Added cover letter (4 pages)
Notes:
Contents: Part A. Transcripts -- Part B. Agenda and presentations.
In the electronic version, this cover page and the cover letter precede Part A only.
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/
November 14, 2014
Ms. Kimberly D. Bose
Secretary
Federal Energy Regulatory Commission
888 First Street, N.E.
Washington, D.C. 20426
Re: Susitna-Watana Hydroelectric Project, Project No. 14241-000
Filing of Initial Study Plan Meetings Transcripts and Additional Information in
Response to October 2014 Initial Study Plan Meetings
Dear Secretary Bose:
By letter dated January 28, 2014, the Federal Energy Regulatory Commission
(Commission or FERC) modified the procedural schedule for the preparation and review
of the Initial Study Report (ISR) for the proposed Susitna-Watana Hydroelectric Project,
FERC Project No. 14241 (Project).1 As required by the Commission’s January 28 letter,
the Alaska Energy Authority (AEA) filed the ISR with the Commission on June 3, 2014
and conducted ISR meetings on October 15, 16, 17, 21, 22, and 23, 2014. Attached as
Attachments A-1 through F-2 are the written transcripts (along with the agenda and
PowerPoint presentations) for these ISR meetings.
During the October ISR meetings, AEA and licensing participants identified
certain technical memoranda and other information that AEA would file with the
Commission by November 15, 2014. In accordance, AEA is filing and distributing the
following technical memoranda and other information:
• Attachment G: Glacier and Runoff Changes (Study 7.7) and Fluvial
Geomorphology (Study 6.5) - Assessment of the Potential for Changes in
Sediment Delivery to Watana Reservoir Due to Glacial Surges Technical
Memorandum. This technical memorandum documents AEA’s analysis of the
potential changes to sediment delivery from the upper Susitna watershed into
the Project’s reservoir from glacial surges.
• Attachment H: Riparian Instream Flow (Study 8.6) and Fluvial
Geomorphology (Study 6.6) - Dam Effects on Downstream Channel and
Floodplain Geomorphology and Riparian Plant Communities and Ecosystems
− Literature Review Technical Memorandum. This literature review technical
1 Letter from Jeff Wright, FERC Office of Energy Projects, to Wayne Dyok, Alaska Energy Authority,
Project No. 14241-000 (issued Jan. 28, 2014).
2
memorandum synthesizes historic physical and biologic data for the Susitna
River floodplain vegetation (including 1980s studies), studies of hydro project
impacts on downstream floodplain plant communities, and studies of un-
impacted floodplain plant community successional processes.
• Attachment I: Susitna River Fish Distribution and Abundance Implementation
Plan, Appendix 3. Protocol for Site-Specific Gear Type Selection, Version 5.
In accordance with the fish distribution and abundance studies, as described in
Revised Study Plan (RSP) Sections 9.5 and 9.6 and in the Fish Distribution
and Abundance Implementation Plan, this appendix establishes the protocol
for site-specific gear type selection for fish surveys. Throughout study plan
implementation, AEA has updated this appendix as needed to provide
consistent direction to all field teams. Version 1 of Appendix 3 was originally
filed with the Fish Distribution and Abundance Implementation Plan in March
2013. That version was updated twice (Versions 2 and 3) during the 2013
field season to accommodate protocol changes that related to FERC’s April 1,
2013 Study Plan Determination, field permits, and lessons learned during
study implementation. Version 4 was the protocol used for the 2014 field
season and was updated with respect to the prioritization of gear use and
based on 2013 data collected. This version herein, Version 5, will be followed
during the 2015 field season.
• Attachment J: Fish Distribution and Abundance in the Upper and
Middle/Lower Susitna River (Studies 9.5 and 9.6): Draft Chinook and Coho
Salmon Identification Protocol. This document established a Chinook and
coho salmon identification protocol to support accurate and consistent field
identification across field teams. It will allow for additional quality control
and assurance of field identification calls and for estimation and reporting of
any field identification error that may occur in future sampling efforts.
• Attachment K: Characterization and Mapping of Aquatic Habitats (9.9),
Errata to Initial Study Report Part A - Appendix A, Remote Line Mapping,
2012. This errata provides a corrected version of map book for Remote Line
Mapping, 2012. The version filed with the ISR (June 3, 2014) used a data
query to build the maps in geomorphic reaches MR-1 to UR-5 that mistakenly
did not include side slough habitat, so that no side sloughs were depicted on
the Appendix A maps 1 through 21. This version was corrected by including
side slough habitat in the data query for geomorphic reaches MR-1 to UR-5.
This version now includes side sloughs.
• Attachment L: Characterization and Mapping of Aquatic Habitats Study 9.9,
Revised Map Book for 2012 Remote Line Mapping. This map book represents
an update to the version published on June 3, 2014 with the Study 9.9 Initial
Study Report and the errata provided concurrently with this filing (see
Attachment K). The maps presented include all macrohabitat and mesohabitat
line identifications available in the 2012 Remote Line Mapping ArcGIS
3
shapefile. This map book should be considered a full replacement for
previous versions and represents the final product for the 2012 remote line
habitat mapping effort.
• Attachment M: Study of Fish Passage Barriers in the Middle and Upper
Susitna River and Susitna Tributaries (Study 9.12), Fish Passage Criteria
Technical Memorandum. This technical memorandum presents a proposed
final list of fish species that will be included in the fish barrier analysis as well
as depth, leaping and velocity passage criteria for selected fish species. AEA
previously consulted with the federal agencies and other licensing participants
regarding the information within the technical memorandum during a March
19, 2014 Fisheries Technical Meeting.
In addition to the technical memoranda and other information identified above,
AEA is filing a short errata (Attachment N) to the Mercury Assessment and Potential for
Bioaccumulation Study (Study 5.7), Evaluation of Continued Mercury Monitoring
Beyond 2014 Technical Memorandum. This technical memorandum, which was
originally filed on September 30, 2014, evaluates the need for continued monitoring of
mercury data beyond 2014 and whether the existing data collection efforts are sufficient
to satisfy objectives for characterizing baseline mercury conditions in the Susitna River
and tributaries (RSP Section 5.7.1). Since the filing of this TM and based upon the
ongoing QA/QC of the data reported in that TM, AEA discovered errors in the TM. The
attached TM corrects those errors. Additionally, the errata corrects corresponding errors
in the Mercury Assessment and Potential for Bioaccumulation presentation presented
during the October 16, 2014 ISR meeting.
Finally, AEA notes that data collected during the Study Plan implementation, to the
extent they have been verified through AEA’s quality assurance and quality control (QAQC)
procedures and are publicly available, can be accessed at http://gis.suhydro.org/isr_mtg. On
November 14, 2014, AEA posted the following data to this website:
• Baseline Water Quality Data (Study 5.5), 2013 QAQC water quality data
and DVRs per the Quality Assurance Project Plan.
• Breeding Survey Study of Landbirds and Shorebirds (Study 10.16),
cumulative 2013-2014 data.
• Characterization and Mapping of Aquatic Habitats (Study 9.9), ArcGIS
shapefile “ISR_9_9_AQHAB_RemoteLineMapping_2012.shp” used to
generate the maps in Attachment L.
4
AEA appreciates the opportunity to provide this additional information to the
Commission and licensing participants, which it believes will be helpful in determining
the appropriate development of the 2015 study plan as set forth in the ISR. If you have
questions concerning this submission please contact me at wdyok@aidea.org or (907)
771-3955.
Sincerely,
Wayne Dyok
Project Manager
Alaska Energy Authority
Attachments
cc: Distribution List (w/o Attachments)
Susitna-Watana Hydroelectric Project
(FERC No. 14241)
Initial Study Report Meetings
October 21, 2014
Part A – Transcripts
Alaska Energy Authority - Board Room
813 West Northern Lights Blvd.
Anchorage, Alaska 99503
Filed November 15, 2014
Susitna-Watana Hydro ISR Meeting
October 21, 2014
SUSITNA-WATANA HYDRO
Agenda and Schedule
Initial Study Report (ISR) Meetings
Wildlife and Botanical (Studies 10.5 - 10.20; 11.5, 11.7 - 11.9)
Alaska Energy Authority - Board Room
813 West Northern Lights Boulevard
Anchorage, Alaska
October 21, 2014
_______________________________________________________
ATTENDEES
Julie Anderson, Alaska Energy Authority
Nate Anderson, Alaska Energy Authority
Earl Becker, Alaska Department of Fish & Game
Martin Bozeman, Alaska Energy Authority
Phil Brna, U.S. Fish and Wildlife Service
Michael Bruen, MWH Global
Sarah Bullock, Bureau of Land Management
Mark Burch, Alaska Department of Fish & Game
Olivia Cohn, Solstice Alaska
Justin Crowther, Alaska Energy Authority
Jennifer Curtis, EPA
Wayne Dyok, Alaska Energy Authority
Alynda Foreman, Louis Berger Group
Andrew Fraiser, Alaska Energy Authority
Graham Frye, University of Alaska Fairbanks
Sandie Hayes, Alaska Energy Authority
Bob Henszey, Fish & Wildlife Service
Janet Kidd, ABR
Kirby Gilbert, MWH
Kim Jones, Alaska Department of Fish & Game
Jan Konigsberg, Alaska Hydro Project
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Susitna-Watana Hydro ISR Meeting
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Brian Lawhead, ABR
Becky Long, Susitna River Coalition
Matt Love, Van Ness Feldman
Todd Mabee, ABR
Lauren McClure, Stillwater Sciences
Betsy McGregor, Alaska Energy Authority
Rick Merizon, Alaska Department of Fish & Game
Sterling Miller, Dunrovin Research
Alan Mitchnick, FERC
Laura Noland, Environ International
Tim Obritschkewitsch, ABR
Sarah O’Neal, Unidentified
Doug Ott, Alaska Energy Authority
Dirk Pedersen, Stillwater Sciences
Alex Prichard, ABR
Laura Prugh, University of Alaska Fairbanks
Casey Pozzanghera, University of Alaska Fairbanks
Tyler Rychener, Louis Berger (for FERC)
Terry Schick, ABR
Nate Schwab, ABR
Chuck Sensiba, Van Ness Feldman
John Shook, ABR
Miranda Studstill, Accu-Type Depositions
Emily Teraoka, Stillwater Sciences
Cassie Thomas, National Park Service
Rachel Thompson, Alaska Energy Authority
Fred Winchell, Louis Berger Group
Ellen Wolf, Susitna River Coalition
Whitney Wolff, Talkeetna Community Council
INTRODUCTIONS:
MR. GILBERT: Okay. Let's get started so we can try to stay
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Susitna-Watana Hydro ISR Meeting
October 21, 2014
on time on the agenda.
Hi. I'm Kirby Gilbert with MWH, and I'm working for AEA.
I'll be moderating these meetings, facilitating this week.
This is the second in a series of meetings on the
Susitna-Watana Hydro project, the initial study report. We've got
three meetings this week. There were three meetings last week.
Maybe a lot of you were involved or participated in it. They were at
the Millennium Hotel, and those were focused on the aquatic studies.
This week is the terrestrial phase, terrestrial resources, wildlife
and botanical. And then we've got some of the physical sciences,
cultural, subsistence, paleontology tomorrow, and then on Thursday,
the remainder of the social sciences and recreation studies.
Just real quick, it's not too full in here, which is great. And
please sign in as you come in. If you haven't signed in, please do so.
We -- if there is any need to evacuate the room for any reason,
we are all to go up the stairs and out the door on the main lobby, and
right up into the north parking lot.
Also there are restrooms on this floor, and if you've been here
before, you have to be a little careful because they've been remodeled
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Susitna-Watana Hydro ISR Meeting
October 21, 2014
and switched, so just make sure you look at the sign on the door. But
they're right outside and around the hall.
So we'll start with some introductions. We'll kind of go
around the room, and then we'll go on the phone.
And just to note, and I'll make this note a couple of times. We
do have a court recorder, Miranda, transcribing. And because of that,
and it makes it all the more important, that everybody state their
name before they make a comment, and so on.
So we'll go around the room, and everybody, if they could at
least introduce their selves. And if you're a contractor, be sure to say
who you're working for, represent, and so on, so we can get
everybody's role all figured out here.
So we'll go around this way. I'm Kirby Gilbert, MWH.
MS. HAYES: Sandy Hayes, AEA.
MR. FRAISER: Andrew Fraiser, AEA.
MS. NOLAND: Laura Noland, Environ.
MR. GILBERT: And Environ, working --
MS. NOLAND: Representing the Fish & Wildlife Service.
MR. GILBERT: Fish & Wildlife Service. Okay. Thanks.
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Susitna-Watana Hydro ISR Meeting
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MR. BRNA: Phil Brna, Fish & Wildlife Service.
MR. MILLER: I'm Sterling Miller from Dunrovin Research.
I'm here representing the Wild Salmon Center and Trout Unlimited.
MS. ANDERSON: Julie Anderson, Alaska Energy Authority.
MS. THOMPSON: Rachel Thompson, Alaska Energy
Authority.
MR. BOZEMAN: Martin Bozeman, AEA.
MR. ANDERSON: Nate Anderson, AEA.
MR. OTT: Doug Ott, Alaska Energy Authority.
MR. MERIZON: Rick Merizon, Alaska Department of Fish &
Game.
MS. JONES: Kim Jones, Alaska Department and Fish &
Game.
MS. BULLOCK: Sarah Bullock, Bureau of Land
Management.
MR. CROWTHER: Justin Crowther, Alaska Energy
Authority.
MS. COHN: Olivia Cohn, Solstice.
THE COURT REPORTER: Miranda Studstill, Accu-Type.
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Susitna-Watana Hydro ISR Meeting
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MR. DYOK: Good morning. Wayne Dyok, Alaska Energy
Authority.
MR. SENSIBA: Chuck Sensiba, with Van Ness Feldman, on
behalf of AEA.
MS. MCGREGOR: Betsy McGregor, Alaska Energy
Authority.
MR. SCHICK: Terry Schick with ABR.
MR. LAWHEAD: And Brian Lawhead with ABR.
MR. BURCH: Mark Burch with Fish & Game.
MR. GILBERT: So we'll turn to the phone now. But can
you -- those on the phone, can you hear okay so far?
MS. LONG: Yeah, we can hear okay. Hi, Kirby. I might as
well start.
This is Becky Long, Susitna River Coalition.
MS. THOMAS: Cassie Thomas, National Park Service. And
thanks for the much better audio than last week.
MR. WINCHELL: Fred Winchell, Louis Berger, contractor
with FERC.
MS. MCCLURE: Lauren McClure, Stillwater Sciences,
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Susitna-Watana Hydro ISR Meeting
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contractor to FERC.
MS. MCGREGOR: Did you get that? Wait.
MR. GILBERT: Can you repeat?
MR. PEDERSEN: Dirk Pedersen, Stillwater Sciences,
contractor to FERC.
MR. GILBERT: Okay. I've got Dirk Pedersen, Stillwater
Sciences. Who was the woman before with Stillwater?
MS. MCCLURE: Oh, this is Lauren McClure.
MR. KONIGSBERG: Jan Konigsberg, Alaska Hydro Project.
Good morning, Kirby.
MR. GILBERT: Hi, Jan.
MR. MABEE: Todd Mabee, ABR.
MR. OBRITSCHKEWITSCH: Tim Obritschkewitsch, ABR.
MR. SHOOK: John Shook, ABR.
MR. MITCHNICK: Alan Mitchnick, FERC.
MR. GILBERT: Hi, Alan.
MR. MITCHNICK: Good morning.
MS. FOREMAN: Alynda Foreman, contractor to FERC.
MR. GILBERT: Okay. We're going to do that roll call again
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Susitna-Watana Hydro ISR Meeting
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after we start up again at lunch. So that's very helpful.
I will try to just remind everybody, there's more room at the
table, but if you're going to speak or comment today, it might help if
you stand up. But we just want to make sure it's clear, and I'll be
checking with Miranda throughout the day a little bit to make sure
that we're -- everybody knows who's talking, because it is hard on the
phone. I was on the phone last week and it was really challenging to
try to listen and follow what was going on.
And also, those on the phone, please don't put us on hold.
Just -- if you have another call, just hang up and dial back in, because
we'll get music or something if you put us on hold. Everybody will.
Okay. Well, today we've got the wildlife and botanical
studies. There are 16 wildlife, four botanical studies, so we have
quite a bit to cover, but we have all day to do it.
So it's broken up. We've got -- the agenda's been out. The
agenda and the presentations through today have been out for two
weeks on the web site.
We're going to try to go through each presentation in no more
than about a ten-minute period, because we're trying to make sure we
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Susitna-Watana Hydro ISR Meeting
October 21, 2014
have time to discuss, not just present it.
The expectation is that people have read the ISR, spent quite a
bit of time, and hopefully have looked at these presentations. The
presentations are intended to be an aid, an overview of the subject
matter at hand for each of the studies.
So I'll go through a few introductory slides, and then Wayne
will have a few remarks, and then we'll go through each of the
studies one by one.
Let's see if I can get this to work here. There we go. Okay.
So these meetings today, these are the initial studies as
required by FERC under the ILP regulations. It's a -- it's really a
check-in point halfway through the two-year study process, and it is
a chance, because this is right out of a regulation, for the licensee and
participants to discuss with AEA and its contractors, to share these
results and any proposals, modifications, questions everybody has on
all the studies as we go ahead. It's a check-in point.
The initial study report was filed June 3rd, and previous to
that, on February 3rd, a part of that was filed. So it's been out there
quite a while, and it's been on the AEA web site for quite a while. It
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Susitna-Watana Hydro ISR Meeting
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is a tremendous amount of work. There's over 8,000 pages for all 58
studies. And today, as I said, we'll be talking about 20 of them, so
quite a few today.
And normally the ILP does not offer this much time, but we've
got quite a bit of time here. So hopefully that's helped everybody, to
be able to digest this information in the area they're interested in.
And then as the year went along, AEA continued to work on
several studies, especially studies with timely data questions, and so
on. And there were some technical memorandums that were filed
and posted on the web site in September, and now those were all in
the aquatic field. There were 16 of them, I believe.
MS. MCGREGOR: Twenty-two.
MR. GILBERT: Oh, 22. Okay. So -- but with that, FERC
had come in and looked at that and heard from a lot of the parties,
and FERC has now extended the schedule a little bit on this review
cycle, and there will be a second set of meetings in January for those
studies that had technical memorandums filed. And those are being
scheduled now in the next week or two for early January.
MR. MILLER: So those aren't terrestrial mammals?
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Susitna-Watana Hydro ISR Meeting
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MR. GILBERT: Pardon me?
MR. MILLER: The second meeting will not include terrestrial
mammals?
MR. GILBERT: Not at this time. Be sure to state your name.
MR. MILLER: Sterling Miller. Sorry.
MR. GILBERT: That's okay. Just to make it easy for her.
Thanks.
MS. LONG: Kirby, this is Becky Long.
I just want to kind of correct what you said about the technical
memorandums. I've counted them. There's 40 technical
memorandums, the supplementals that came out in September. And
also, a lot of it deals with geomorphology, which I don't know if I
(indiscernible - interference with speaker-phone). [8:39:13]
MR. GILBERT: Yeah. So aquatic, water, anything to do with
the riverine environment. So yeah, I'm summarizing it incorrectly to
say aquatic.
MS. MCGREGOR: So just --
MS. LONG: It was an impressive data dump of about 1,800
pages.
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Susitna-Watana Hydro ISR Meeting
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MS. MCGREGOR: This is Betsy McGregor with AEA.
I just want to clarify that there are 22 technical memos. There
may have been appendices. They may have been broken into pieces
due to size, to make it easier to download, but there were 22
technical memos, plus one on the Chulitna Corridor.
MR. GILBERT: Okay. So this slide here is just talking about
what's next, and that's what we're going to try to talk a lot about
today, what's next.
But this is the current schedule for the next -- next item after
these second -- another set of small meetings in January, and other
small meetings that AEA's working on scheduling now. AEA will
file the summary of all the meetings with FERC and put it up on the
web site.
And then one month later, February 21st, is the chance for all
the licensing partners -- participants -- to file their formal comments
and study requests about all the review that's gone on and reactions
to the meetings, AEA's notes.
And then another month goes by, and in March, it's a chance
to -- for AEA and others to file back comments.
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Susitna-Watana Hydro ISR Meeting
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And finally, FERC gets to make a study-plan determination,
just like they did with the original study plan, revised study-plan
determination, to make any adjustments to the studies or methods
and modifications, and so on, for the following year, for 2015 work
studies.
And then we're still on the same schedule for filing an updated
study report, which is a culmination of the studies, and that's
February 1st, 2016.
So that's the current schedule as it is that FERC’s come down
with.
Okay. As I mentioned today, we're halfway through here.
We're in the botanical and wildlife studies.
And then tomorrow, as I mentioned, we have the physical
sciences, subsistence, cultural, and paleontology.
Thursday, social sciences, quite a few studies there, too, and
the recreation, and esthetic studies.
And then AEA will be announcing shortly the other meetings
that are planned for aquatic.
And again, we want to try to make these meetings as useful to
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Susitna-Watana Hydro ISR Meeting
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everybody, so it is about a chance to discuss, which means
conversation, and it's a chance for everybody to participate and ask
questions, that hopefully you read the ISR.
There is some work that Brian and his team will talk about that
went on in March, ADF&G 3/20/14. We're going to talk a little bit
about that.
There are no technical memos, so I don't think that's helpful to
anybody. But hopefully people really have read the ISRs. But we do
have the contractors here to go over the highlights and what the plans
and variances are, the plans for completing the study.
And then the idea being, this is a chance, if licensing
participants think there are going to be modifications or new studies,
to make those -- to get those comments ready to file with FERC so
FERC can consider them in their study-plan determination.
Most of you are -- you should be familiar with the ISR. It's a
little different structure than a normal ISR. It's in three parts.
The Part A is the part that was filed in February. That is the
bulk of what happened in 2013, without the plans for completing the
study.
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Susitna-Watana Hydro ISR Meeting
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Part B of each ISR, each of the 58 studies, is -- was any
supplemental information that enhanced the Part A, or corrected
errata from the February filing, so that was a nice chance to bring
that up to par.
And then -- and then Part C is the one that's really important
here. That summarizes the plans to complete the study, and I think
that's a lot of what's going to happen today.
There were variances described in the first study season, and
then there could be modifications -- continued variances or
modifications that AEA and the contractors are proposing for
completing the studies in the next season. And that's what we are
discussing today.
The last -- we'll go through a little bit about the approach in
here, and then you can see more about the -- what we have on the
wall here, the criteria for making a study request. These are right out
of the regulations, and they're also on the PowerPoint slides.
As I mentioned, each of the study team is going to be -- Brian
and a lot of his team are going to go through each of the studies in
the order on the agenda. We're going to try to stick to the agenda
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Susitna-Watana Hydro ISR Meeting
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and -- try to stick to the agenda and the time, and the leads are going
to try to focus on the thing -- the variances.
We've had to summarize a little bit of the results, the
highlights of the results, and discuss importantly the proposed
modifications that they'd like to carry through for the next study
season.
And there also are some decision points that were explicit in
the ISR and in the previous study plans about where data's come
together, and a decision needs to be made on which way to go with
the study. There's a few of those here and there.
And then really, it's about everybody participating and asking
questions or giving us any proposed modifications for AEA and its
contractors, to consider and get your input. So that's really what we
want to do today.
Okay. The last slide -- last few slides, as I mentioned, are the
same as what we have up on the wall, and those are right out of the
regs, in terms of what -- what the criteria FERC has in terms of
requesting a modification to a study, any changes, by the
request -- well, we do -- we do refer back to the study-plan
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Susitna-Watana Hydro ISR Meeting
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determination, because that is the starting point, and then the study
proceeded. So anything that wasn't in sync when that study-plan
determination and the methods were approved is considered a
variance, so that's the way -- often we will be referring back and we
have access to the study plan and other materials, if we need to pull it
up today.
And then this gives the details on the content of the study
request, if the licensing participant wishes to file or make any
proposals. So these are the criteria we're all supposed to follow,
okay?
So if there's not any questions, I'll turn it over to Wayne.
MS. THOMAS: Kirby, this is Cassie Thomas.
And I am just wondering if AEA plans to update its schedule
tab on the project web site, which still doesn't reflect a change in the
ISR review and comment schedule.
I think it would be very useful if that were to be updated so
that everyone would know when the various deadlines are.
MR. GILBERT: Yeah. Yes. Good request. That's -- that
seems very reasonable. We'll get at that.
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Susitna-Watana Hydro ISR Meeting
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Okay. Unless there's any other questions, before we start right
in, Wayne has a few things he can share with us maybe, to help us all
today.
MR. DYOK: Thanks, Kirby.
And good morning, everyone, and welcome.
We still have five chairs. I know Kirby had mentioned that.
So we'll let you sit in the back row there, but if you're going to be
talking, we would like to ask you at that point to come to the table,
just so everyone on the phone can hear better and the court reporter
can, you know, accurately get your remarks.
I want to take a big-picture perspective here for a second and
look at: What are we trying to accomplish with these studies?
There's really two purposes.
First of all, the Federal Energy Regulatory Commission needs
this information for their environmental analysis, and the agencies
will need it for their permitting or their conditioning
recommendations for the -- for the license. So it's important that we
do this -- collect this baseline information for the environmental
analysis.
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Secondly, we need to use this baseline data to assess project
effects and to develop protection, mitigation, and enhancement
measures. So let's keep that in mind as we go through.
And some of you are new faces that I haven't seen before. So
just as a reminder, a couple of years ago, in 2012, we had a major
collaborative effort to develop what we considered to be the right
studies, and these are pretty robust, you know, study plans that were
developed.
We also collected some information in 2012. Last year, 2013,
was our first year of conducting studies per the FERC study-plan,
you know, determination. And as Kirby mentioned, we filed that
initial study report on June 3rd, and that's really the subject of today's
meeting.
But it includes not only work that was collected in 2013. It
includes work that was collected in 2012, and to the extent
appropriate, even information that was collected in the 1980s.
This year, we had an opportunity to collect additional
information. And primarily, that was because we didn't have full
access in 2013, but we do have that access now. So we went in there
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and we filled in data gaps.
And to the extent that that's relevant, hopefully that
will -- information will come up and be touched upon here today, as
appropriate.
We are going to be getting out, you know, the schedule.
And, Cassie, thank you very much for your comment. Once
we get done with these initial study report meetings, we'll lay out a
schedule for, you know, future meetings and just what the new
big-picture schedule is.
So over the next three days, I want to encourage all of us
to -- you know, to work together. Let's try to understand the data,
what it means, and in particular, how we're going to be using this
information in decision-making. We work together. I think we can
identify appropriate, you know, study-plan modifications.
So with that, I'll just turn it back to Kirby and we'll get right
into the heart of the matter here.
MR. GILBERT: Okay. Good. That was a great overview.
Any other questions? Anybody on the phone? You guys
could hear that? Okay.
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So we'll turn it over to Brian Lawhead from ABR, and he'll go
through these various bird studies.
MR. LAWHEAD: Okay. Thank you, Kirby.
And if at any time -- I'll echo Kirby's remarks. I did try to
listen some last week, and it was pretty bad. So if you can't hear on
the phone, particularly questions of someone in the back of the room,
please let us know and we'll correct that.
All right. I'm Brian Lawhead with ABR. I'm the wildlife
program lead. And we're going to start off with three bird studies.
These are fairly involved, a lot of data collected, and so we
want to make sure we give adequate time to them at the beginning of
the session today. We're going to start with waterbird migration,
breeding, and habitat use, and that'll be presented primarily by Tim
Obritschkewitsch.
The next will be surveys of eagles and other raptors with John
Shook, and then we'll end this session before the break with landbird
and shorebird migration, breeding, and habitat use.
I should mention that there's a migration element to all three of
these studies, and it's made for a little bit of complexity in how the
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data were presented. Waterbird migration, breeding, and habitat-use
study included, as will -- we'll get into a little bit more detail on it --
but it included a radar and visual migration component that wasn't
restricted solely to water birds. It included all species of birds.
And then there was also a migration survey component for the
raptor study that also included all species of birds. So I just wanted
to give you a little bit of context there.
And with that, I will turn it over to Tim. Tim is a research
biologist with ABR who's been responsible for the aerial survey
component of this study.
If we -- if we drill into the radar and visual migration studies
and there are questions that we can't answer, I'll have to get in touch
with the study lead for that task, who is in Oregon and had an
unavoidable conflict today. But, if necessary, we can get them on
the -- on the line later and deal with any issues that people have or
questions that we aren't able to address.
So with that, I will turn it over to Tim. And I'm going
to -- Tim is in Fairbanks. Several of our presenters are in Fairbanks
today, and so I'm going to run the slides, so bear with me.
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Tim, you just prompt me when you want me to go on. I'll just
move to the next slide here.
WATERBIRD MIGRATION, BREEDING, AND HABITAT
USE (STUDY 10.15)
MR. OBRITSCHKEWITSCH: Okay. Thanks, Brian. How
am I -- how am I coming through here? Am I clear?
MR. LAWHEAD: Yeah, you sound good.
MR. OBRITSCHKEWITSCH: Okay. Good. This is Study
10.15, the Waterbird Migration, Breeding, and Habitat Use study.
For the purposes of this study, waterbirds broadly includes
swans, geese, ducks, loons, grebes, cranes, gulls, and terns.
The study has several broad objectives. The objectives
included documenting the distribution, abundance, habitat use, and
seasonal timing of waterbirds migrating through, and breeding
within, the project area.
They also included reviewing available information on food
habits of piscivorous waterbirds in the study area, in support of the
mercury bioaccumulation study. That's Study 5.7, which was
discussed at an earlier meeting.
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To meet these objectives, the waterbird study had the
following components.
Next slide.
MR. LAWHEAD: Go ahead. There'll be a little bit of a delay
when I advance it.
MR. OBRITSCHKEWITSCH: Oh, okay.
During spring and fall migrations in 2013, aerial surveys were
flown throughout the study area at regular intervals, and
ground-based radar and visual surveys were conducted from a
site -- from a site northwest of the proposed dam site.
During the breeding season, two breeding-population surveys
were performed. For Harlequin Ducks, two surveys were conducted
during pre-nesting and two during brood-rearing. These surveys
were conducted along rivers extending up to ten miles outside the
three-mile-buffer study area.
Brood surveys were conducted in water bodies within a
one-mile buffer around the locations and alignments of project
infrastructure, including access roads and transmission corridors.
A literature review on food habits and diet was conducted to
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identify appropriate species in the study area for mercury sampling.
Finally, in the field, nests and broods of piscivorous birds were
recorded in connection with the mercury study, although very few
nests were discovered. I'll touch on that a little bit later.
There were five variances to the methods outlined in our study
plan.
Fewer surveys were flown during migration than were
originally projected. Mostly this happened because the number of
surveys was dictated by ice conditions and breeding chronology, so
this -- the variation in the number of surveys -- was expected.
But also, as indicated on this slide, surveys generally took
more than a day to complete, and this spread the surveys out a little,
and also contributed to the lower number of surveys.
We replaced the term "breeding-pair survey" with
"breeding-population survey," which is a better reflection of the data
that we collected and presented, because it includes flocked birds as
well as the pairs.
Let's see. We restricted our Harlequin Duck surveys to ten
river miles beyond the study area buffer. Many tributaries contain
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suitable habitat well beyond that distance, but it would have been
logistically unfeasible to continue the survey beyond ten miles.
The choice of ten river miles for the cutoff was based on the
linear home range for Harlequin Ducks during pre-nesting and brood
rearing.
Originally, the study plan called for ground-based visual
surveys conducted by a single observer, then a modification
recommended by the U.S. Fish & Wildlife Service called for the use
of four observers, and this modification was accepted by FERC.
But, after further consultation and clarification, the Fish &
Wildlife Service dropped its recommendation of four observers, and
this study met its objectives using a single observer.
Finally, we did not acquire tissue samples in 2013. This
objective was based on the expectation that nests of piscivorous birds
might be found opportunistically, but the aerial surveys were
designed to detect breeding pairs and broods, not specifically nests,
which would require careful inspection of shorelines and islands.
As a result, only one nest was discovered in 2013. It was a
Common Loon nest. But we did locate a number of broods of
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piscivorous birds, and the water bodies that they occupied can be
targeted for future nest searches in conjunction with Study 5.7.
Next slide, please.
The 2013 study area is shown in purple and includes the
three-mile project area buffer for aerial lake-to-lake waterbird
surveys. It includes a rectangular block that you can see east of the
Watana Reservoir for breeding population -- breeding-population
surveys that were conducted using transect methods and the ground
survey area for radar and visual surveys, which is indicated by the
circle near the proposed dam site.
This slide is somewhat inaccurate, in that we dissolved the
doughnut hole between the Chulitna and Gold Creek corridors, and
we did actually survey the water bodies in that area.
This particular figure includes the Denali East Corridor,
shaded in red, which was added in 2014 and was not part of the 2013
survey. This figure does not show the river segment survey for
Harlequin Ducks, but you'll see the Harlequin Duck rivers in an
upcoming slide.
The study site for ground-based radar and visual surveys was
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located on the bench about a half-mile northwest of the proposed
Watana Dam site.
Next slide, please.
Diurnal and nocturnal flight information were collected using
radar -- using radar during spring and fall migration. Data from
ground surveys were not limited to water bodies, as Brian mentioned,
or to waterbirds, as Brian mentioned earlier.
The range covered by the radar was 1.5 kilometers for
small-bodied birds, such as passerines and shorebirds, and
6 kilometers for large-bodied birds.
Diurnal visual observations were conducted using binoculars
and spotting scopes between sunrise and sunset, and nocturnal
audio-visual surveys were conducted using either binoculars or
night-vision goggles, depending on light conditions during the first
two to three hours of nocturnal radar sampling.
The combination of aerial surveys and ground-based visual
and radar surveys provided a pretty broad range of complementary
baseline information during spring and fall migrations.
Next slide. The aerial surveys documented abundance, species
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composition and water bodies used by waterbirds throughout the
spring and fall, essentially acting as a series of snapshots every five
to six days. Whereas the ground-based surveys described the
movements of birds within the area, including passage rates and
flight directions, altitudes and behaviors.
In spring, aerial and ground surveys were conducted from the
third week of April through late May or early June, and in fall they
occurred from mid-August through mid-October.
The ground-based surveys provided a broad base of
information.
Next slide.
For example, visual surveys documented relative abundance
and peak occurrence of species groups moving past the study site,
which in some cases correlated well with peaks in numbers seen
during aerial surveys.
Detailed movement information described in the previous slide
is well beyond the scope of this presentation, but some highlights:
during spring, visual observers recorded over 8,000 birds,
representing 89 different species. And during fall, about 6,500 or so
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birds were observed, representing 51 different species.
Nocturnal radar surveys documented primarily westerly
movements during spring and easterly movements during fall.
As with the ground-based data, the information we gathered
during aerial surveys is too extensive to address in detail for this
session.
Next slide.
This figure is an example of the type of information we got
from migration surveys. If you can't see it very well, I'm not sure
how it's showing up there, but all of these figures are pulled from the
ISR.
This is a subset of waterbird observations during the spring of
2013, showing the maximum number of waterbirds observed in each
water body. Essentially this -- this suggests where some of the local
hot spots were, at least one point during the spring.
In 2013, you can see that many of the hot spots were along
rivers, especially early in the season, and in particular the Susitna
River, but several other rivers were also used.
As soon as open water became available on water bodies, birds
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moved from rivers to lakes and ponds. 2013 was a late year, and this
transition happened in late May that year.
Similar data were collected during the pre-nesting, brood
rearing, and fall migration periods, which can be analyzed by species
and dates to develop a comprehensive picture of waterbirds in the
area throughout the season.
Use of rivers and streams by Harlequin Ducks are also
displayed geographically.
Next slide.
Harlequin Ducks -- Harlequin Duck surveys identified habitats
and specific river segments used by pre-nesting Harlequin Ducks.
Harlequins were found on many of the rivers we surveyed that
appeared to have appropriate habitat, particularly on some rivers
south of the reservoir area that you can see on the east side, also on
the Susitna River, and on some of the slower-moving streams of the
central Denali Corridor there.
Similar surveys were conducted for Harlequin Ducks during
the brood-rearing period. I’ve only scratched the surface of the data
we presented in the ISR for aerial surveys, but overall, 32 waterbird
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species were recorded during spring and fall migration surveys, and
brood surveys covered 499 water bodies, and identified at least 227
individual broods from 24 different species.
A small set of modifications were proposed for the 2014 aerial
surveys.
Next slide.
The Denali East Option was added in 2014. That was the area
shaded in red on the study area slide, around the alternative access
road and transmission corridor.
2014 surveys were conducted with the same variances as in
2013. The components related to mercury analysis have been
consolidated under Study 5.7, and one of the proposed modifications,
the third one on this list, "conduct second year of ground-based
visual and radar migration surveys" will not be conducted. We'll
touch on this a little bit more in the decision-point slide in a couple
of minutes.
There was a new modification to the study since the ISR.
Next slide.
The Chulitna Corridor was not surveyed in 2014.
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A second year of aerial surveys was conducted in 2014.
Next slide.
Very briefly, surveys again occurred from late April through
mid-October. Methods were the same as they were in 2013, so the
corresponding table for 2014 would be identical to the one that you
see here, except for the actual dates and numbers of surveys, which
are, again, dependent on timing of break-up and nest initiation each
year.
The most obvious difference so far between 2013 and 2014
was that break-up occurred much earlier this year and birds occupied
water bodies and initiated nests earlier.
Fall migration surveys were completed just a few days ago,
and data for 2014 are still being proofed and analyzed.
Next slide.
MR. LAWHEAD: I can talk about this one. This is -- most of
the slides say decision point since the ISR. This is actually a
decision point that was in the revised study plan and the -- and it
pertains to the radar/visual migration surveys.
There is a lot of text here, but in short, the radar/visual
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migration monitoring task was conceived as a single-year effort in
2013 to try and get a handle on the -- you know, the species
composition, the timing, the flight altitudes, flight directions, passage
rates, movement rates. It's a pretty intensive study. There was over
100 days in the field, basically around-the-clock monitoring.
And the purpose of that was to get a good description of the
nature of the migration in the area, and then to compare that with
other data from similar studies elsewhere in Alaska, which is all
summarized in -- both in the ISR, and then there's also an
Appendix T in Part B of this study that sort of assembled the
migration study elements from the raptor and waterbird studies and
compares those with other comparable data from elsewhere in
Alaska.
So based on this, AEA has proposed to not conduct a second
year of monitoring. And this was discussed in technical work group
meetings on March 6th, and again somewhat on April 9th, I believe.
Do you want to take over again, Tim?
MR. OBRITSCHKEWITSCH: Yeah. Steps to complete the
study, finally.
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The study plan required two seasons of aerial survey, and the
second season was completed in 2014; the last fall migration survey
was flown a few days ago. Data analyses will be completed this
winter, and results from both seasons will be synthesized and
included in the USR.
And that's all I have. Last slide.
MR. GILBERT: Okay. That was a lot of material. Thanks,
Tim and Brian.
So now is the part where we try to do this in all the studies, is
go around and see what comments people have.
And in particular, of course, what we're trying to do, and
FERC and everybody, is to find what agencies and licensing
participants have in terms of modifications. If they agree with the
modifications or have other modifications to the studies, now is a
great time to start talking about them.
So we try to go through this, and we've kind of just structured
it so Fish & Wildlife Service, federal agencies, BLM, do you guys
have comments, modifications in mind on this study?
State your name.
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MS. NOLAND: This is Laura Noland with Environ,
representing the Fish & Wildlife Service.
And my comment doesn't relate to a modification. It relates to
how you're going to fulfill the commitment that AEA made to
conduct fur and feather sampling, which I know has been moved to
5.7, but we still feel that you need to collect the data in the field to
adequately determine what the baseline of mercury is in that system.
MS. MCGREGOR: So just to clarify, that comment -- we
want to make sure that comment's made on Study 5.7.
MS. NOLAND: We made that comment on 5.7.
MS. MCGREGOR: And that's where -- that's where we'll
address it is on the mercury study, on 5.7. It's not actually -- in the
ISR, we changed it from components of these various studies
because these were just the data collection component of it, and we
put it -- we consolidated everything into Study 5.7, which is the
mercury assessment.
MS. NOLAND: I think we understand that, but we see that
there's a component of data collection to -- responding to this study
that needs to be done.
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MS. MCGREGOR: Right. And that's been moved to
Study 5.7. So I just want to clarify that we'll address that comment
in Study 5.7 and not in these individual studies. Because it's to meet
the objectives of that study and not each one of these various bird
studies.
MS. NOLAND: So are you saying you're not going to respond
to that question today at this meeting?
MS. MCGREGOR: Well, I can give the same response we
provided in the meeting last week when we covered Study 5.7. We
are waiting to see what the pathways analysis tells us as to whether
or not we have a need to collect data on the piscivorous birds. Based
on what we've already collected in the fish samples, we have a little
bit -- sampling with piscivorous mammals is difficult because of the
availability, just the abundance. They're pretty low numbers. We
have a few samples there.
And we're going to wait to see what the pathways analysis tells
us before we determine whether or not we need to sample. We did
have extensive consultation in March regarding how we would
sample the birds and adding blood component instead of just the
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feathers.
If we move forward with sampling birds, we will follow the
methods that we outlined in March. We also identified the target
species that would be sampled based on their -- the abundance of
distribution in the study area.
MR. BRNA: This is Phil Brna with Fish & Wildlife Service.
Fish & Wildlife Service will be providing written comments
on the ISR. We've had some concerns, especially about the mercury
stuff. I will provide written comments.
We also have internal review of all these bird studies, and
well -- to be honest, neither Ellen nor I have looked at any of our
internal reviews because we focused on the fish and the water stuff,
so we'll be reviewing those and providing formal comments.
And we are going to -- we are going to -- well, we are going to
probably recommend that FERC require -- continue to require
sampling. Whether we do the blood stuff or the feather stuff, that's
still up in the air, but we have -- I guess Ellen and Wayne had a
conversation with FERC last week, so we're going to follow up on
that.
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And we might want to suggest some kind of additional
discussion here so we can try to work this out.
Is that your understanding, Wayne?
MR. DYOK: Well, I think clearly in this particular case,
there's, you know, different perspectives, and I think further
discussion is probably, you know, valuable. I'm not sure, since we
don't have the pathways analysis yet. Maybe that's something that
will be a precursor to decisions.
So what we'll do, as Betsy said, we'll get that pathway analysis
done, and then if you have a schedule for when that's going to be
done, Betsy.
MS. MCGREGOR: No.
MR. BRNA: So is that going to be a technical memorandum,
an additional one?
MS. MCGREGOR: Maybe. I mean, somehow I'll have to
memorialize that information and provide it to people for review.
MS. STEELE: Marie Steele from the Department of Natural
Resources.
So at the end of the day, will you be able to identify the
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baseline mercury levels so that you can measure the changes, if there
are, in fact, any changes in mercury post-project?
MS. MCGREGOR: Yes. So they sampled the water column,
the pore water, the sediment, the fish, and they collected a few
piscivorous mammal samples.
They did not move on to the bird sampling yet because we
were waiting for the pathways analysis to be complete to determine
whether or not it was necessary.
MS. STEELE: To follow on then, you will be able to -- for all
these different species of animals, whether they're fish or bird or
beavers or whatever, you will have a baseline of the current mercury
concentrations?
MS. MCGREGOR: We'll have baseline data for what we
actually collected, what we -- what samples we actually collected,
and then they're using a pathways analysis to look at how it's going
to accumulate in the system.
MR. BRNA: Yeah, there won't be any baseline data for birds
because no birds were sampled.
MR. GILBERT: Can you guys hear on the phone? I just want
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to make sure.
UNIDENTIFIED MALE: Not very well.
MR. GILBERT: Okay. So you guys be sure to try to speak up
in the back, and you might just stand up even, because they are part
of the meeting, and so we want to make sure.
So Marie Steele from DNR is asking about which species they
would have baseline mercury level data for by the time we're done.
MR. BRNA: So this is Phil Brna, Fish & Wildlife Service.
And I said there will be no baseline data for birds if no birds
were sampled.
MS. STEELE: And this is Marie Steele from DNR.
And I'm just trying to close the loop. So you have your
pathways analysis that may or may not identify the birds. It's not
necessary to sample birds. But I want to make sure that the
validation is going to be there to, in fact, support the pathway
analysis. It says birds don't need to be sampled.
MS. MCGREGOR: Yes. And that will be in Study 5.7, not
this study. So just want to clarify where people should direct those
comments and where we will address those comments.
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MR. GILBERT: Okay. So what other kind of comments?
Anything from BLM or --
MS. BULLOCK: Yeah. Just a question --
MR. GILBERT: State your name again, just --
MS. BULLOCK: Sarah Bullock, Bureau of Land
Management.
MR. GILBERT: Thanks, Sarah.
MS. BULLOCK: I didn't see --
MS. MCGREGOR: You need to speak up.
MR. GILBERT: Can we ask people to sit at the table here,
Sarah, you and Phil and Laura, since you guys have comments?
Otherwise, it's so difficult for the people on the phone. So please
come to the table.
MS. MCGREGOR: Thank you.
MS. BULLOCK: The Chulitna Corridor, I didn't see it
explicitly stated why it was dropped from the study again.
MR. GILBERT: She's asking about the Chulitna Corridor.
Maybe you or Betsy --
MS. MCGREGOR: You can talk to it.
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MR. DYOK: I couldn't hear you, Sarah.
MS. BULLOCK: The Chulitna Corridor, why was it dropped
from the study?
MR. DYOK: Why was it dropped from the study? In the
letter that we filed with the Federal Energy Regulatory Commission,
we had a couple of primary reasons.
The first and foremost was the effect on the two anadromous
streams -- Indian River and Portage Creek -- where most of the
salmon spawning in the middle river takes place in those two
streams. And then from an engineering perspective, it's more prone
to snow slides.
MS. BULLOCK: Okay. So basically the Chulitna Corridor is
kind of at the bottom of the three possibilities?
MR. DYOK: Right, right. And there's also a lot more private
lands around the Chulitna Corridor, as well. So those are probably
the three primary factors, with the biggest one being the potential
effect on the anadromous salmon.
MS. BULLOCK: Okay. Thank you.
MR. GILBERT: Okay. How about other comments on the
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bird species? Anything statewide? Okay.
Does anybody on the phone have some comments about the
waterbirds study?
MS. WOLFF: I have a quick question. This is Whitney with
the Talkeetna Council. Can you just specify when you did that last
flight? You said a few days ago.
MR. LAWHEAD: October 19th.
MS. WOLFF: October 19th. Okay. Thank you.
MR. OBRITSCHKEWITSCH: Yeah. This is Tim.
That actually was the 17th and the 18th, so the 18th was the
last day on that last survey.
MR. LAWHEAD: Yeah, okay. So the slide we prepared for
the talk was done before the surveys actually ended.
MR. OBRITSCHKEWITSCH: That's right. It was scheduled
for the 17th through the 19th, and that's what we put on the slide.
But because there was so much -- there was so much ice now in the
study area that the survey took fewer days than we scheduled.
MS. WOLFF: That's actually what I was asking: Was this
when you initially scheduled it? It seems late.
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MR. OBRITSCHKEWITSCH: It seems late?
MS. WOLFF: Well, I was wondering if this is the day you
scheduled it in the original revised study plan.
MR. OBRITSCHKEWITSCH: We --
MR. LAWHEAD: I can speak to that, I think.
We didn't really -- I don't think we identified specific dates.
We kind of said until mid-October. It's sort of a balancing act as to
where to cut these migration surveys off because the water bodies
freeze progressively, you know, down from higher elevations, and
the number of birds you detect continues to drop. They tend to
accumulate on the last few large lakes that are open. So there's some
judgment involved in that.
But yeah, there was still -- I think there was still a bit of open
water in the large lakes, particularly Stephan Lake, Murder Lake, and
I think maybe Deadman Lake.
Is that right, Tim?
MR. OBRITSCHKEWITSCH: Yeah, Deadman Lake, Big
Lake, there was still some on Clarence Lake. Some of the other
deeper water bodies still had some open water, and there was
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still -- there were still some birds out there by mid-October, the
numbers have dropped off quite a bit, but there's still a few birds
around.
So yeah, where to cut off the surveys is sort of a balancing act
on that one. But we had originally planned it to be through
mid-October, and that's -- and that's what we did.
MS. WOLFF: Okay. Thank you.
MR. GILBERT: Okay. Any other questions, proposed ideas
for waterbirds?
MR. LAWHEAD: Hearing none, we'll move on to the next
study, 10.14, Surveys of Eagles and Other Raptors. And John Shook
will be leading this presentation from Fairbanks.
So again, John, I'll switch the slides for you.
SURVEYS OF EAGLES AND OTHER RAPTORS
(STUDY 10.14)
MR. SHOOK: All right. Thanks, Brian.
Thank you for your attendance.
The raptor studies have six major objectives, which include to
locate and determine the status and productivity of nesting raptors;
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estimate the project effects on productivity; estimate the effects on
habitats by delineating raptor habitats; to conduct fall and winter
raptor concentration studies; assess the collision potential of
proposed power lines to raptors; and finally, to produce
information -- to provide information on fish-eating (or piscivorous)
raptors for the mercury study.
Next slide.
To meet these objectives, the following components were
implemented. You can see here are the five major study
components, which we will discuss in the following slides.
You can see that three major field efforts are in bold. Note the
picture on the right of raptor migration data collection during our
very pleasant spring of 2013.
Of these study components, we have three variances.
Next slide.
Variances for the raptor study were limited to study area
modifications, land-access delays for migration surveys, and salvage
permit delays for the mercury sampling of fish-eating raptors.
Next slide.
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Next we'll look at some summary results from the 2013 ISR.
Occupancy and productivity surveys have been performed from 2012
to 2014 and entail most of the field work and results of the raptor
studies.
Additionally, these data likely produce the most important
information. Of note first, to guide you through this table, first is
the -- the first column on the left, total nests, represents the number
of nest structures built by that species. And this is different than
nesting -- the number of nesting raptors. This is very relevant to the
eagle permitting process.
Two, raptors are territorial. Even though they don't breed in a
given year, they may occupy more than one nest structure. And
raptors, especially Golden Eagles, build and occupy multiple nests
within a territory.
And finally, raptors often leave ambiguous occupancy
evidence, which was especially true in 2013. The numbers in
parentheses indicate additional possible territories that had an
unknown occupancy status. You can see the Golden Eagles are
nest-building machines. They often occupy many nests, even if not
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breeding in that given year.
In 2013, many eagles were still occupying their territories but
did not breed, probably due to the very late spring and low
availability of prey, for example, snowshoe hares early in the season.
Both of these environmental factors likely contributed to
lower-than-average nest success in 2013.
By contrast, 2014, there were only five unknown occupancy
territories, with 21 incubating pairs.
You contrast that with what you see in the table -- first line of
the table.
Next slide.
The next map displays status and distribution of all eagle nests,
and the map speaks volumes. There are quite a few Golden Eagle
nests, which are the yellow icons, and the occupied structures are the
stars.
The red icons are the Bald Eagle nests. Again, stars are the
occupied Bald Eagle nests.
Next slide.
The next map displays the remaining other raptor nests. Of the
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other raptors, Common Ravens in gray and Peregrine Falcons in dark
green are the most common , with a few Gyrfalcon and Goshawk
nests.
It is noteworthy that researchers did not locate any nesting
Peregrines during the 1980s Susitna studies; thus, we may be seeing
a population recovery or range expansion as we've seen elsewhere in
Alaska.
Next slide.
After the occupancy surveys, the second largest effort was the
raptor migration studies. Migration surveys were conducted for one
month each season to assess the collision potential for all raptors.
Thus we did not separate migrants from non-migrants.
Bald and Golden eagles are the most common nesting raptors;
therefore, many of these individuals may not likely be migrant.
The red dots are the migration observation points, while the
adjacent rosette diagrams show the direction of travel and the total
number of raptors for each season. If you look at the inset example,
each block equals one bird. Thus, four raptors flew due south, two of
which were Golden Eagles, one unknown eagle, and one other raptor.
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Overall, there were relatively low numbers of migrants. And
as you can see, our observers were quite excited to record each raptor
observation. Brian can point out several of the empty rosette
diagrams where no raptors were recorded.
Typically in the northern Alaska Range in spring, we would
expect westerly movement; therefore, the bars would be stacked up
on the left, whereas in the fall, we would expect easterly movements.
While some locations do show higher use, a clear, non-random
pattern of bird movements was not evident. The late spring of 2013
probably made this a below-average year for raptor migration.
The remaining four slides -- I'm sorry. The remaining four
studies are represented in the final results slide.
MR. GILBERT: Hey, John, I just want to remind you to try to
keep it prompt, because we learned last week and previously that we
want to make sure we have plenty of time for discussion, even to the
point where we could go back if people ask about results. So I just
want to you keep it moving, because I want to try to make sure you
focus on the variances and plans for completing the study in a short
time. We're trying to keep them to ten minutes, so I just want to
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make sure.
MR. SHOOK: You bet. This is the last results slide.
We conducted high-intensity sightability surveys, woodland
raptor surveys, foraging and roosting surveys, and finally we
delineated cliff nesting habitats.
Next slide.
Next we look at proposed modifications. The three proposed
modifications in the ISR include the addition of the Denali East
Corridor, which was surveyed in 2014. The mercury analysis
objectives were moved to Study 5.7, as discussed earlier. The
woodland raptor survey has increased survey intensity within random
blocks.
Next slide.
And additionally, there are two more new proposed
modifications since the ISR. One, the Chulitna Corridor was
eliminated. And two, further study of fall and winter forage and
communal roosting raptors may no longer be warranted because two
years of surveys were completed and no major concentrations were
located.
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Now, briefly, let's look at what was completed in 2014. In
2014, only the occupancy and productivity surveys were performed.
Surveys were modified in response to corridor changes. We
provided raptor nest-avoidance information to reduce disturbance,
and we provided the project with another year of data for permitting.
Looking ahead, here are the remaining steps to complete the
study. To complete the raptor study, the team will conduct nest
occupancy and productivity surveys, sightability assessment of these
surveys. We'll continue delineating Bald and Golden eagle nesting
habitats. And finally, we will conduct spring and fall migration
surveys along potential power line routes.
This concludes the presentation on raptors, and I'll turn it over
to Mr. Gilbert.
MR. GILBERT: Okay. Good. Thanks. That's right on track.
So that's a snapshot of the raptors and -- eagles and raptor
study.
So again, start with federal agencies' comments, modifications,
docs. Did you guys like the study?
MR. BRNA: I didn't say that.
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MR. GILBERT: Do you have comments or are you
anticipating comments?
MR. BRNA: Yes, we're anticipating comments.
MR. GILBERT: But you don't have any --
MS. MCGREGOR: So are we going to discuss any comments
at the meeting?
MR. BRNA: We're not going to discuss any comments at the
meeting.
And we previously mentioned last week that we're not
prepared to talk about the 2014 stuff at all at this point because that's
outside the FERC schedule. And we will have comments later,
probably. We're hoping to have comments later this year.
MS. MCGREGOR: So how about the material that's in the
ISRs, the 2013 information and the proposed modifications?
MR. BRNA: Well, we're not prepared to discuss them today
because we haven't -- like I said, for -- we were focused on the other
stuff. We had internal reviews done and we haven't completed those
yet. So when we do, we will provide formal written comments.
MR. GILBERT: Okay. Well, it's nice to have them today,
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you can discuss them, if that helps you guys at all.
MR. DYOK: Do you have any questions for us then to
elaborate on anything that we've presented here, Phil?
MR. BRNA: No, I don't have any questions.
Do you have anything, Laura?
MS. NOLAND: Nope.
MR. GILBERT: Okay. How about others? Nate, anybody on
the phone, proposed ideas for these studies or comments?
MS. FOREMAN: This is Alynda Foreman, representing
FERC.
I had a question about whether or not you anticipate
continuing or the need for collection of incidental data from other
project studies. Regarding the muskrat push-ups, I noted that you
were -- that the bird folks kind of took data for the muskrat survey
that was done incidentally.
And I wondered if you had plans to continue collecting the
incidental data, or I guess I should ask this during the aquatic
furbearers. I wanted to catch the bird people before we went into the
furry ones.
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MR. LAWHEAD: Yeah. I mean, incidental observations are
recorded when they're made. We haven't -- we haven't tried to
assemble those from the waterbird surveys from the -- for 2014 yet,
but that's something we can look at during the analytical stage, data
reduction stage.
And we do plan to conduct a muskrat survey next spring.
MS. FOREMAN: Okay. Thank you.
MR. GILBERT: Okay. Other comments, questions?
MS. WOLFF: I have a quick question. This is Whitney with
the Talkeetna Community Council.
Do we get -- I haven't read the 2014 data, but do we get
elevations on those nests that you cited on that?
MR. SHOOK: Yes. Yeah, we have elevations for all nests.
MS. WOLFF: Great. Thanks.
MR. KONIGSBERG: Hi, this is Jan Konigsberg. I have just a
general question.
I understand -- and I didn't really study the ISR on the raptors,
but I was -- I want to make sure I understood what you said, that in
2013, it was anomalous weather conditions that you think decreased
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migrant -- migration over the study area, raptors?
MR. SHOOK: Yes, it potentially did. Because we had very
cold and snowy conditions, which are not conducive for many
migrants, but especially raptors that often rely on thermals to soar
during migration.
And also raptors need to eat many of the other migrants -- the
other bird migrants -- and also mammals that might not be available
under that snow pack, as they emerge later. So a combination of
events in the spring likely decreased what we saw for raptor
numbers.
MR. LAWHEAD: Delayed it. Delayed it until after the
surveys ended, you mean?
MR. SHOOK: Well, yes. Yes. Possibly delayed it, yes.
MR. KONIGSBERG: So that was my next question. But
there was no -- the study didn't continue past the date to see if there
was a delayed migration or if they just didn't show up at all?
THE COURT REPORTER: Can you have them state their
name for me, please?
MR. SHOOK: Yeah. The raptor study did not continue, but
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the radar and visual migration study did, and they did
collect -- continue to collect raptor migration-specific data after the
raptor migration survey was completed. We do have some of that
information from the radar site.
MR. GILBERT: Just to make sure, Jan, state your name again,
because the court recorder is just having a little difficulty.
That's Jan Konigsberg.
Keep going. Don't want to interrupt you.
MR. KONIGSBERG: Well, that answered my question.
Thank you.
MR. GILBERT: Okay.
MS. LONG: Hi, this is Becky Long from SRC.
I just -- could you clarify again? I'm sorry; I didn't quite get it.
Did -- so you have not made a conclusion that the migration was
delayed or didn't show up? You just don't know? Thank you.
MR. SHOOK: Yes. It's hard to make a definite conclusion,
especially from only one year of studies. So we don't have the spring
migration data -- we have nothing to compare it to for this part of the
state. We are not aware of any migration studies that have occurred
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in the Alaska Range.
The migration was certainly -- there's a lot less numbers than
in other migration studies, other studies in the northern Alaska Range
and other places in Alaska. So it's hard to -- it's hard to tease out the
differences in the spring in 2013.
MR. LAWHEAD: I'll make the observation that the -- the
delay -- the late break-up in 2013 was also something that we looked
at with regard to waterbirds. And the effect seems to be there that it
telescoped the arrival of birds so they were all -- they appeared to
have arrived and initiated nests closer together than they ordinarily
would have, particularly with regard to the dabbling ducks, which
tend to be a little earlier, and the diving ducks, which tend to be a
little bit later.
So the conclusion was that it didn't -- didn't affect the species
composition or numbers necessarily, but that it did change the timing
of movements.
And again, the raptor migration surveys were conducted on a
month-long period ending in mid-May, but the radar/visual migration
surveys near the dam site continued until the beginning of June.
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MR. GILBERT: Okay. Anything else on raptors, eagles?
Okay.
Well, I think we'll go ahead then and cover the last bird study,
and then take a break, as our agenda has us on a schedule that looks
pretty good.
So, Terry, are you going to cover the land and shorebirds?
Justin is getting that ready. The study is 10.16.
And it goes through, to summarize it, efficiently, and
especially modifications. But people think about it, and if you think
you have questions, this is a good chance. There's a lot of effort that
went into these meetings, so anything anybody has to ask or suggest
about these studies would be great.
LANDBIRD AND SHOREBIRD MIGRATION, BREEDING,
AND HABITAT USE (STUDY 10.16)
MR. SCHICK: Okay. This is Terry Schick with ABR, and
I'm going to talk about landbird and shorebird migration, breeding,
and habitat use.
I should probably say right up front, this is primarily a
breeding and habitat-use study. These were point-count studies,
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surveys of riverine corridors, and some lacustrine water body
surveys. The migration component for landbirds and shorebirds was
done under Study 10.14, which Tim talked about earlier today,
primarily the radar and visual observations at the proposed dam site.
MR. GILBERT: Okay. Click the mouse on the presentation
and then it will go.
MR. SCHICK: Okay. So objectives, there are a number of
objectives here. These are all in the ISR, so I'm just going to hit the
high points here.
The overarching objective of this study was to determine
distribution, abundance, and habitat use of breeding landbirds and
shorebirds in those areas that would be affected by this proposed
project. So in each of the proposed transmission line/road corridors,
and reservoir area, and in the region for the proposed dam site and
associated infrastructure.
Habitat association information obviously would be collected
to help with this analysis of project effects, and we were going to
look at the changes in distribution and abundance and habitat use by
comparing to historical data.
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Components, again, all of these are in the ISR. The biggest
component of this study were the point-count surveys at randomly
determined locations throughout the study area, early morning point
counts for landbirds and shorebirds. We also did focused riverine
transect surveys along stream and river courses, and in lacustrine
habitats to try and determine abundance and distribution of those
species, which are typically under sampled traditional point-count
surveys.
We also did a nesting swallow colony survey in the reservoir
inundation zone in 2013. Migration surveys, as I mentioned, were
part of Study 10.15, the Waterbird Migration, Breeding, and Habitat
Use Study.
Comparisons with historical data will be done after the final
year of study. And the mercury assessment component of this study
is now in Study 5.7, which we discussed previously.
There were a number of variances for this study. Again, all of
this is in the ISR, so I'm going to hit the high points here.
We used a different method to determine the location of
point-count plots within the study area. Frankly, I think the
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alternative method is better than our originally proposed method.
What we're doing now basically mirrors what is being done in the
Alaska Landbird Monitoring Survey, or ALMS, as most people know
it.
There are a number of other variances. The bigger ones here
are down at the bottom in bold. We used a helicopter survey
platform for the nesting swallow survey instead of a boat. This
greatly increased survey efficiency and spatial coverage, so that was
definitely a positive thing for this study.
It also allowed us to expand the survey area, so we surveyed
for nesting swallows both within the reservoir and reservoir dam and
camp area, and then in a two-mile buffer surrounding each of those
areas.
This is a map of the point-count locations and the riverine
transect surveys in 2013. You will see that a big portion of the
reservoir area and the Gold Creek Corridor were not sampled
because we didn't have access to CIRWG lands in 2013. We do now,
and we did sample there in 2014.
Then up in the northwestern corner of the Denali Corridor,
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there is also a block that was unsampled in 2013 because we didn't
have vegetation data from 1987, which was used as the strata to
allocate plots in a random stratified allocation procedure. We do
have data for that area now, from the mapping that's being conducted
for this project in Study 11.5, which we'll talk about this afternoon.
And we sampled in both the northwestern Denali Corridor and on
CIRWG lands in 2014.
So briefly, what did we find? This is a multi-species study, so,
you know, putting tables up here, it wouldn't even fit on this slide.
There were a lot of species recorded, so I'm just going to hit the very
high points here.
In the point-count surveys, we had 53 landbirds reported.
Eight of the very most common species were Fox Sparrow,
White-crowned Sparrow, Common Redpoll, Yellow-rumped
Warbler, Varied Thrush, Savannah Sparrow, Ruby-crowned Kinglet,
and American Tree Sparrow.
So you can see that I am repeating the word "sparrow" a
number of times here. Four of the eight species that were the most
abundant were sparrows. So the landbird community is definitely
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dominated numerically by sparrow species in this area.
We did preliminary density estimates using distance analysis
for the 2013 data and were able to calculate densities for 38 of those
53 landbirds, 72 percent, which is pretty good for a single year of
data. We collected over 1,300 point counts in 2013.
Shorebirds, this is a different story. They are much more
uncommon than landbirds, and that's just typical of that species
group.
Only 11 species of shorebirds were recorded. By far, the most
common species on the point-count surveys were Wilson's Snipe.
Spotted Sandpipers were also very common, but primarily on
riverine point-count plots. American Golden-Plovers and Lesser
Yellowlegs were also quite common.
Because of their uncommonness and the lower numbers of
observations for shorebirds, we had insufficient data in 2013 to
calculate densities for any of those shorebird species.
Riverine survey results and lacustrine survey results. On the
riverine surveys for landbirds we saw species typical of vegetated
riparian habitats, Blackpoll Warbler, Wilson's Warbler, Fox Sparrow,
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and especially Northern Waterthrush.
A single species of shorebird, Spotted Sandpiper, perhaps not
surprisingly, accounted for 98 percent of the observations of
shorebirds in riverine areas. This is “the” habitat for Spotted
Sandpipers.
Lacustrine surveys for landbirds. Common species were
American Robin, Rusty Blackbird, Bohemian Waxwing, and
Savannah Sparrow. Rusty Blackbird and Bohemian Waxwing, of
course, are common species in bog habitats.
For shorebirds, Red-necked Phalarope accounted for
25 percent of the shorebird observations. Red-necked Phalaropes, of
course, use lacustrine water bodies directly, so that's to be expected.
Wilson's Snipe, Lesser Yellowlegs, and Least Sandpiper were also
common on the margins of lacustrine water bodies.
This is just a depiction of the location of the swallow colonies
located in 2013. Most of those were along the Susitna River proper,
but some were on drainages, clear-water drainages running into the
Susitna River.
In 2013, 26 colonies were located within the study area.
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Almost all of those were Bank Swallow colonies, but two of them
were of mixed species, Bank Swallows and Violet-green Swallows.
Many colonies were located on existing, steep, permanent
cliffs, as in the photo above. Others were located on freshly exposed
bluffs right along the Susitna River after the break-up in 2013. So
every year there's probably some movement of swallow colonies in
different areas.
Colonies ranged in size from one to 354 burrows, with an
average of 37 burrows per colony.
So summary of results since the ISR: In May and June in 2014,
we again did point-count surveys, riverine and lacustrine-focused
surveys. As I mentioned, in 2014, that included surveys in those
areas that were unsurveyed in 2013. Surveys were not conducted in
the Chulitna Corridor. And all of this -- these data will be reported in
the USR.
Proposed modifications to Study 10.16: These four really are
variances. I'm not going to go into these. These are described in the
ISR.
We have some additional modifications that are also listed in
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the ISR. The Denali East Option corridor has been added to the
study area.
In 2013, we did point-count plots along the riverine transect
surveys. We dropped those in 2014 because stream noise was a
fairly significant problem in 2013 in recording all landbird species on
the point-count plots on the riverine transect surveys.
For those riverine transect surveys going forward, the metric
of bird abundance is going to be linear densities, birds per kilometer
of stream length. And for lacustrine surveys, the new abundance
metric will simply be the total number of birds recorded per water
body. And the mercury assessment work is now under Study 5.7, as
we've discussed a number of times.
This is the study area going forward for 2015, which includes
shaded in red the Denali East Option Corridor, and also includes the
Chulitna Corridor, which we expect will continue to be unsampled in
2015.
We have one additional new modification that is not in the
ISR. For the riverine transect surveys in 2014, we incorporated line-
transect sampling techniques to allow us to do distance analysis for
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the riverine survey data, as well. And if this works out as planned,
we should be able to have corrected densities, corrected for
detectability, for the riverine transect data as well as the point-count
data.
This applies only to those birds using shoreline habitats, that is
shorelines and littoral habitats. Landbirds were also recorded in
vegetative riparian habitats but getting distances and angles to each
landbird on a transect survey is pretty impossible. This is why they
invented point-count surveys to begin with.
And then the Chulitna Corridor has been dropped, as we
discussed.
Current status: In 2013 and 2014, field surveys were
completed as planned in the ISR. Some surveys were not done in
2013 in some areas, but those were resurveyed or surveyed for the
first time in 2014. They will be surveyed again in 2015, and giving
us two years of data for all areas in the study area.
In 2013, we did 1,365 point counts. In 2014, we did 1,209.
Those are big numbers for point-count surveys, if you guys are
familiar at all with point-count survey studies. We had a goal of
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doing 800. We exceeded that in both years.
Riverine and lacustrine surveys were repeated as planned in
2014. Swallow colony surveys will be completed in 2015.
Steps to complete the study in 2015: We will again do
point-count surveys, riverine transect, and lacustrine surveys. We'll
do a final estimation of breeding population densities using distance
analysis. Habitat-use analyses will be conducted to provide the
information for the evaluation of wildlife habitat-use study. We'll
talk about that later today.
The second year of swallow colony surveys will be completed
in 2015.
And that's all I have.
MR. GILBERT: Okay. That was a good summary. Sounds
like [9:56:25] successfully.
What do we have on this study? Does it make sense? Any
comments? Any questions?
MR. BRNA: I have one question. This is Phil Brna at the
Fish & Wildlife Service.
So the variances, I think it was slide 14, for the variances not
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discussed in the ISR. How are we going to find out about those,
other than this presentation? Is there a tech memo or we're going to
talk about those in January?
MR. SCHICK: Well, yeah.
MS. MCGREGOR: One second. I just want to clarify, we're
not discussing these topics in January. The January meetings are for
the 14 studies that we put out tech memos for. So if there is
additional information --
MR. BRNA: Yeah, we're not prepared to talk about 2014
studies today.
MS. MCGREGOR: Right. So at least if we can talk about --
MR. BRNA: So we are on the assumption that all 2014
studies were going to be talked about in January.
MS. MCGREGOR: Just for the 14 studies that --
MR. BRNA: Oh, okay.
MS. MCGREGOR: In FERC's letter, it's for the 14 studies to
cover the tech memos that were provided. So it would be great if we
could talk about at least the results that are in the 2013 today.
MR. BRNA: Well, we didn't review any 2014 studies.
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MS. MCGREGOR: So today we would talk about the 2013
information.
MR. BRNA: Yeah. And we're not prepared to talk about that
here.
MS. MCGREGOR: Okay.
MS. LONG: Hi, this is Becky Long.
It would seem to me that if any -- if the applicant put that in
the additional information about 2014 data that wasn't in the ISR in
variances, then they should also -- these studies need to be talked
about in the January ISR meeting.
MS. MCGREGOR: And we're open to that, if we can hear the
specific topics that people would like to discuss. So far we're not
getting any discussion on what was presented in the ISRs. So it's
kind of difficult to know what additional information we may need to
provide for 2014, when we are not really having any discussion on
the 2013 material that's been available since February and June.
MR. KONIGSBERG: Jan Konigsberg.
I think it's getting a little confusing. My assumption was that
the 2014 -- any studies in 2014 that were conducted after the first
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2013 study are second-year studies and would be part of the USR,
right?
MS. MCGREGOR: They will have to be fully reported in the
USR, you are correct, Jan.
MR. KONIGSBERG: So just to make this a little clearer, that
the tech memos for 2014 do include 2014 studies?
MS. MCGREGOR: Yes. So there were 22 tech memos that
were issued that covered 14 studies. Those were all the riverine and
aquatic-related resources.
The January meetings, the whole reason why FERC put out an
extension was because of those tech memos, the material in those
tech memos, and that's what we're limiting the January meetings to
cover.
If there are specific studies that people have concerns about,
then we can talk about that. But this is the ISR meeting for these
terrestrial studies. This is where we're supposed to be talking about
the material that was presented and provided in February and June.
MR. KONIGSBERG: Okay. I just wanted to make sure that
at least, in my mind, it's clarified.
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MS. LONG: Hi, this is Becky Long again.
But also last week, AEA stated that there was going to be more
material coming out by -- on deadline of November 15, and it would
seem that it would be necessary to discuss that at the January
meetings. I mean, we can do specific discussions. I get it. We don't
have to go through, like, a whole presentation. But it seems like
some of that material will need to be covered.
MS. MCGREGOR: We're going to need feedback during this
meeting of the specific studies and the specific information that you
guys are looking for.
At the end of the last set of meetings, AEA covered the
approach for the January meetings, that we would have specific
targeted meetings in December about specific topics only. And
they're just technical meetings. They're not TWG meetings. We
won't be providing material two weeks in advance. It's just not
feasible, given the holidays and the time frame between these
October meetings and the January meetings.
But FERC was very clear in their letter that the January
meetings are to cover the material presented in the tech memos. So
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we’re -- AEA is in the same position -- we're happy to go over and
provide additional information, but we're not obligated to until the
USR. So it really has to be a directed effort and we need to
understand what specifically people are looking for.
MR. GILBERT: Yeah. Hopefully the slide presentations are
an aid, because there are some things that they continue to do that
they are talking about, but those need to be reported in the USR.
Does that make sense?
MS. MCGREGOR: And these slides were posted 15 days ago,
and they do provide an overview of the information that was
gathered in 2014. So that should help people understand what was
conducted in 2014.
MS. LONG: Hi. And thank you for that, Betsy. This is
Becky Long again.
I really totally forgot about you're talking about the technical
meetings in December. I'm sorry. I did forget about those.
MS. MCGREGOR: And that's okay. And we're -- as we said
when we wrapped up the last set of meetings, AEA is working with
our contractors. We are identifying what we think are specific areas
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that we thought would be beneficial for us to follow up on in
December. We're going to work with the agencies and look at that
information. They're going to help prioritize.
But we really have a very narrow window of opportunity
between the holidays and January 7th meetings. So it's kind of
limited, what we can discuss.
MR. MILLER: Sterling Miller.
Would you clarify about the December technical meetings?
And are those going to be to discuss recommendations that are made
for study design changes that are made at this meeting?
MS. MCGREGOR: No.
MR. MILLER: So when will recommendations for study
design changes that are made at this meeting be considered?
MS. MCGREGOR: Well, we would discuss them now, today.
That's the point of today's meeting.
And then we are obligated to file that -- the meeting summary
in January, and then you can provide formal comments at the end of
February, and then we'll respond to those comments at the end of
March.
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I don't know if you can pull up the schedule, the FERC
schedule, Justin.
MR. GILBERT: Yeah. That was in -- in the introductory
slides. So today is a chance to talk about the modifications AEA has
proposed in the ISR, and that's the thing. And if you guys have any
other comments about those or there are other modifications you
would like. So that's today.
And then AEA will file the notes to the meetings in January,
and then it was outlined in those introductory slides that they -- and
then you can file comments about a month later, February 21st,
formal comments.
MR. BRNA: Comment on the --
MR. GILBERT: Modifications, progress to date, any
rationale, any other modifications? But that's what these criteria are
all about, for that filing. They were predominantly structured in a
way that FERC expects it to be, and then -- and then AEA can
respond to those comments about a month later, and FERC will make
a determination based on all the record that's brought together at that
time.
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MR. BRNA: So this is for information in the ISR. But if
there's information not in the ISR, like the 2014 stuff, then we're
going to talk about that in 2016 at the USR meeting; is that correct?
MS. MCGREGOR: No.
MR. GILBERT: No. FERC extended it here. FERC extended
it to allow this -- the 2014 work to be captured. That was the intent, I
believe, of the --
MS. MCGREGOR: That's correct.
MR. GILBERT: I don't know if they want to comment.
MS. MCGREGOR: Yes. We're anticipating that you
will -- there has been an extension of time beyond the normal ILP
process that is sufficient to provide comments on what was gathered
in 2014, whether it was presented in a tech memo or it's provided in
these presentations.
MR. BRNA: Oh, in the presentations.
MS. MCGREGOR: Uh-huh.
MR. BRNA: These?
MS. MCGREGOR: Yep.
MR. DYOK: 2014 or 2013?
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MS. MCGREGOR: 2013 and 2014. This is getting the 2014
information on the record.
And FERC was also clear in their letter, 2014 is a study year.
It's a year of study plan implementation.
MR. WINCHELL: This is Fred Winchell, Louis Berger,
representing FERC.
And maybe I can weigh in on my understanding of FERC's
intent, is that the January meetings are to review the additional tech
memos to best inform the study modifications that we made for that
year or for the following year studies. And so I believe that FERC's
intent is to consider the information that's in those tech memos, some
of which are proposed study modifications, so that the last -- the
2015 studies can be designed based on the best information available.
That is my understanding of FERC's intent in that letter.
MR. BRNA: So how about for information that's not
presented in the tech memo but is presented in these presentations?
MR. DYOK: Can I suggest --
MR. BRNA: Can that be discussed in January?
MR. DYOK: Can I suggest that we take a break here and then
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reconvene in 15 minutes here?
MR. GILBERT: Yeah. Because then maybe they can talk
about it a little more. So I think we get the idea here, the
presentation being the only place you've got new information on this
day.
MS. LONG: But just -- but just to kind of wrap up, AEA
is -- you know, basically what we're saying is that there's just not
going to be another meeting.
It's not like you can't comment on the 2014 data that won't be
covered at the January meeting. We can comment on that, and then
FERC will make a decision. But it's just that there's not going to be,
you know, a special additional meeting.
MS. MCGREGOR: That's correct, Becky.
MR. GILBERT: And you can ask questions about it today.
That's the idea.
So we'll take a break now and come back and try to keep on
schedule. Because we do have six more studies before lunch. So if
everybody can try to get back here by 20 after, we'll try to start right
at 20 after.
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(Off record.)
MR. GILBERT: Okay. Hello, everybody on the phone, we've
got everybody back in here. We're going to start up again.
We're going to go through about six studies on mammals, big
game. But first let's -- just to kind of wrap up from the previous
discussion, Sara Fisher-Goad has some AEA remarks about some
plans moving ahead, that may even help bridge this gap with
everybody, and then we'll continue.
MS. FISHER-GOAD: Thanks, Kirby. It's Sara Fisher-Goad,
executive director of AEA.
I was actually at the water resources studies for most of the
time at the Millennium last week, and I really appreciated the
dialogue and the discussion that occurred between the contractors,
the federal resource agencies, the state resource agencies, and AEA's
team.
I guess I'm a little confused. There doesn't seem to be the
same level of interaction and discussion about the 2013 information
today, and so I guess, you know, one, I'd offer, please come to the
table. There's plenty of room here. Please engage in the discussions.
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I -- I guess I'd like to just encourage, you know, where there are
questions with respect to the studies, the AEA team and the
contractors are prepared to discuss, and we want to make sure that
these meetings are productive.
I think the additional meetings that were offered through last
week were the results of, you know, some very good discussions
between the biologists and the research professionals, so I encourage
that same type of discussion here. We want to make sure that these
meetings are productive and that the data and information is useful
for decision-making. So please participate.
That's all. Thanks, Kirby.
MR. GILBERT: Thanks.
MR. BRNA: Can I make a comment? And I will just -- Phil
Brna, Fish & Wildlife Service.
So I will apologize on all the water resources stuff and all the
fish stuff. AEA provided money for the Services to have contractors,
and that's why we were so well-represented there, and that's why we
had so many things to talk about.
On the wildlife stuff -- and we're just focused on birds -- the
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Fish & Wildlife Service had a biologist reviewing all that stuff, and
we've got draft reports from her. She took another job, so we had
nobody here. We had nobody -- no person that has even looked at
the wildlife study. So it's hard to comment on it.
Ellen was supposed to be here today. I wasn't supposed to be
here. She had some endangered species emergency, so here I am, so
that's the -- that's the reason.
MR. GILBERT: Okay. Well, thanks for coming, so that
helps.
Okay. Let's go into the big game, because I know Sterling
mentioned at the break he has a lot of comments, a lot of discussions.
So I think we've talked about that. We'll try to keep these
presentations really short, and you can always go back and look at
the slides, because the slides have been posted for awhile.
So, Kim, you're first on moose? Caribou.
CARIBOU DISTRIBUTION, ABUNDANCE, MOVEMENTS,
PRODUCTIVITY, AND SURVIVAL (STUDY 10.6)
MS. JONES: Hi, everybody. This is Kim Jones from the
Alaska Department of Fish and Game.
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And I am the principal investigator on the caribou, moose, and
sheep studies. So I'm going to go through this pretty fast. If you
have any questions, I can always go back to it, but most of this is in
the ISR. And also, these presentations have been available online for
a while, so I'm not going to read the slides to you.
So here are the study objectives as listed in ISR, and the study
components also listed in the ISR.
And one variance that we talked about in the ISR is just simply
a naming convention. Initially when the study plan was written, we
were optimistic that we would be able to go out and say, hey, this is a
Delta caribou and put a collar on it and call it a Delta, and this was a
Nelchina and put a collar on it and call it a Nelchina.
But after we put all our collars out on our Delta and Nelchina
animals, they kind of did their own thing and went to where they
were going to go, and we realized we weren't really that good at
identifying species -- or sorry, collars based on where they were
captured.
And part of that we've also learned is that there's a lot of
variation and movements in individual animals in a year, and they're
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taking on what we call different wintering strategies. And so animals
that migrate east in the winter we're calling part of the Eastern
Migratory Group. And again, that's just a wintering strategy
describing their method for that year.
And those that winter more in the study area, we're calling the
Western Group. And again, this is just a naming convention, so we
don't think it will affect our ability to meet objectives.
But I also just want to clarify that some individuals were in the
Western Group in one winter, and then in the next winter they were
in the Eastern Migratory Group. So this doesn't describe an animal,
but more describes their wintering strategy for that year.
Another variance is this is -- this is more of a clarification.
One of our objectives in the study plan was to document productivity
and survival of caribou in the project area. And our original study
plan wasn't really clear on how we were going to do that, so we just
added in a little bit of clarification there. And we have been
conducting these parturition surveys for caribou in 2013, and we also
completed them in 2014.
Also here's a table of all the collars that were deployed. All
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collars were initially deployed by October 2012, and we've had
additional capturing events since then to redeploy collars from
animals that have died or dropped their collars.
And the number of collars out in the study area is also
supplemented by management captures that involve putting collars
on five- and ten-month-old calves every fall. And we actually just
completed putting 20 more collars out on Nelchina calves.
These figures are also from the ISR, and this is just to give you
a quick overview of the kind of data that we're collecting. And this is
from our telemetry flights that we're conducting monthly to biweekly
to twice a week, depending on the time of the year, which is all in the
ISR, and showing what parts of the study area the caribou are using
during these different times of the year.
And then this is using our satellite data, and so the satellite
data is great because it follows the animals all the time and we don't
have to go out and track them. And it shows that a large proportion
of the herd migrates out toward Canada in the spring, where they will
winter, and then -- sorry, the fall, they migrate in the fall, where they
will winter. And then in the spring they come back to the calving
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area. And then during the summer, they'll kind of hang out around
the study area, and then in the fall they'll -- most of them will migrate
east again, with the Western Group staying in the study area.
So, variances to be carried forward is the naming convention I
mentioned and the caribou parturition flights.
And also ADF&G already proposed and AEA supported
removing the GPS collars from the animals that the satellite collars
have been out for two years and their battery life is kind of at the
end, and so the -- we removed a lot of those collars and replaced
them with VHF collars last week, and we'll remove the rest of them
in April and replace them -- and put a whole new batch of satellite
collars out.
And we will also continue telemetry, radio-tracking flights into
2015.
And this image here is just to show you some of the variation
in data that we're getting. These are the June 2013 movements in
red, and the June 2014 movements in blue.
And so basically in 2013 that was a really late spring migration
to the calving grounds, which is pretty unprecedented for the
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Nelchina herd, and it was really interesting to document. Because
typically by the middle of May, most of the cows with calves and the
herd are on the calving grounds, shown in this big kind of clumped
area down here.
But in 2013, they were having their calves as far east as the
Copper River, and they didn't even -- some of them didn't even make
it to the calving grounds before having their calves, which is a really
interesting year. So we have a lot of variation in movements, which
is pretty typical for a caribou.
So in order to complete the study, we're going to continue
telemetry through 2015, we're going to remove, refurbish, and
redeploy the GPS collars that I mentioned, and then we'll do the
analysis and have all of that information in the updated study report.
So if anybody has any questions on caribou?
MR. GILBERT: Yeah. So now's the chance to have a
discussion. And again, we'll try to start with federal, state -- go
ahead, Sterling.
MR. MILLER: That movement slide that you showed, I didn't
see any movements north into the other side of the Alaska Range for
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the Delta herd.
MS. JONES: That's because we do not have any satellite
collars on the Delta herd.
MR. MILLER: Oh, I thought you said these were VHS collars
(sic) -- or VHF collars.
MS. JONES: This map in particular is from satellite collars.
MR. MILLER: Oh, all right.
MS. JONES: Yeah. So we don't have any satellite collars on
what you would call conventional Delta animals. All -- but we do
have -- there's a lot of VHF collars on those, and we do monitor them
very closely, documenting when they come south of the Alaska
Range, how long they stay south of the Alaska Range, whether or not
they're having calves down there, and how much they're mixing with
the Nelchina herd, and then when they go back north, if they do.
And some don't. Some come down and join the Nelchina and
migrate east with them, and we've seen a lot of different strategies
out of those animals.
MR. MILLER: So as you are aware, the Delta herd is a much
smaller, more precarious herd than the Nelchina herd and is being
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managed much more cautiously. So when are we going to get the
information on the Delta herd animals and their movements?
MS. JONES: Well, the information will not be mapped until
the updated study report. We didn't really feel that it was relevant to
go into a lot of data analysis and enter our conclusions until we had
all the data in front of us.
But I can tell you the majority of what we call the
conventional Deltas that were collared north of the Alaska Range
with VHF collars, that they're coming down just before calving, and
almost all of them are staying north of the Denali Highway, and they
actually hang out right in this kind of area, up along these glaciers,
like right up on the glaciers. I went and flew recently and took a
look at them.
And then typically they'll stay down there. And then right
before our conventional Nelchina count July 4th, they typically move
north.
But this year, being caribou, they decided to take a different
strategy, and they're still there. But they haven't really been -- they
haven't been mixing as much with the Nelchina. They've mostly
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been staying, like I said, north of the Denali Highway there.
But there are the occasional Deltas that come down and they
just mix right in with the Nelchinas and don't ever go back north.
And we do have one conventionally collared Nelchina VHF, that she
actually goes back and hangs with the Delta for the rest of the year.
But that's pretty much the timing and extent of the mixing that we've
seen.
MR. MILLER: Thank you very much. I forgot to identify
myself, but maybe I'll give -- I will just mention that I am Sterling
Miller. I'm here to provide some comments on terrestrial species for
the Wild Salmon Center and Trout Unlimited. They mostly have
expertise in fisheries, so they've hired me. I'm a consultant to
provide comments on the terrestrial species.
I also had a 21-year career with the Alaska Fish & Game
department, and I participated in all five of the studies conducted by
the Alaska Fish & Game department in the early 1980s and was the
principal investigator of one of those studies. And I'm an affiliate
professor of wildlife at UAF and University of Montana, and I'm up
here from Montana.
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So that's who Sterling Miller is. And so the -- the -- I just
wanted to clarify that the more information being presented so far,
except what you've just done orally on the Delta Caribou herd
movements, except for that one you mentioned that had a collar, or a
GPS collar I think, that did move north of the Alaska Range; is that
right?
MS. JONES: Oh, VHF, yeah.
MR. MILLER: Oh, VHF collar?
MS. JONES: That's correct.
MR. MILLER: And so we don't have the information on
which to evaluate the movements of the Delta herd at this time to
evaluate, so that's just an observation.
The other question I have is I'm sure you're familiar with the
earlier studies in this area done by Ken Pitcher.
And Ken didn't even really recognize that the Delta caribou
herd was part of this mix of animals, because you only find that out
by putting some collars on north of the Alaska Range and then
following them south. If you put out your collar south of the Alaska
Range, you won't -- you won't catch that, because Delta herds will be
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going north where you're not listening for them.
MS. JONES: Right. And they're mostly down there during
calving and you don't want to collar animals --
MR. MILLER: Right. So that's probably why Pitcher missed
it, because the collars were not put out there.
But my general comment has to do with the complexity of the
herd structure in this area. And I'm just wondering if you would
agree with the statement that the herd and group complexity in this
particular area, around the Watana Dam structure, is extremely
complex. Because not only are there Delta animals, as we now
know, and Nelchina animals; there's a resident group of caribou
from, you know, the Chulitna that's over there, and they're mostly
residents, plus the Cantwell groups.
Are those considered herds now, or are those -- and
particularly, if that northern Denali access route is chosen for access,
it will go through the range of those two sub-groups, and they would
both be impacted.
So I guess my more general question is, do you think you've
adequately sorted out the complexity of herd and group structure that
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will be impacted by the proposed project by just classifying these
caribou into two different groups?
MS. JONES: Yeah, that's a good question, Sterling.
And so first I want to clarify is, again, the Eastern Migratory
and Western Group is just a naming convention we're using to
describe wintering strategies, and we're not naming these animals.
We're not breaking down the herd conventions, anything like that.
It's just a way to describe two different wintering strategies.
But the question is -- that Sterling has, is that Pitcher, in the
'80s, found a lot of what he called subherds, Nelchina caribou, and
within the project -- surrounding area. And so I guess we went into
this with an open mind thinking, okay, there's a lot of little subherds
in here that use these areas year-round, and we knew that in the
winter that in the study area, there were some animals that stuck
around. And so we would assume from the '80s studies that they
were subherds.
But what I've actually found is that instead of an animal
staying in the -- in what I would call a subherd and not intermixing,
that animals just take different strategies every year. And there has
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been a lot of movement.
For instance, in April 2012, when we put out the initial collars,
we put out a bunch of bull collars right out of Cantwell, and the plan
was in April of 2014 to go and take those bull collars off out of
Cantwell.
Well, in April of 2014, they were all in Canada. So -- and
basically what we're learning is I don't -- I don't want to speak too
much about the data because we haven't gone into the in-depth data
analysis that we will for the updated study report, but what we have
found is that we're not really seeing what I would classify as
subherds at this moment. We're just seeing different animals taking
different strategies.
But it is true that -- that it is complex and that different animals
use different parts of the study area each year, and that during
the -- so that basically what we're seeing is very large component of
the Nelchina herd is only using the study area primarily between
calving and fall migration.
But there is a component of the herd that we're still trying to
quantify that uses the project area year-round, and we'll get at that a
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lot more when we do all of our spatial analysis for that study for it.
But I do believe the important question is here that we are
collecting the right data to meet that objective and to get at that
answer.
MR. MILLER: Well, I'm glad to hear that, because it's not
stated in the objectives that you're going to try to get these sub-group
or subherd things. So it was unclear to me that you were looking for
that. And so I'm very glad to hear that you are.
MS. JONES: Yeah, uh-huh. And again, we were just trying to
keep an open mind in the beginning because we weren't clear
whether there were subherds or not.
MR. MILLER: All right. If I may continue?
MR. GILBERT: Yeah, sure. And especially things, you
know, because we -- if we run out of time, anything to do with the
plans for completing the study and the modifications. So go ahead.
MR. MILLER: Okay. Did I -- you know, initially the initial
study plan called for two years of study. But I heard you say in your
presentation that you're going to continue for a third year of study
monitoring that; is that correct?
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MS. JONES: That's correct. Actually we put the collars out in
2012, and we're going to continue monitoring through May 2015.
So yeah, we'll have more than the two years of study that's
typically allotted to these FERC-type processes.
And one of the main reasons is, is we have the collars out
there, and it just makes sense to keep monitoring the animals while
the collars are on them, so we've just asked for an extension to
continue that monitoring.
MR. MILLER: Oh, I'm glad to hear that, because I do think
it's very important that it's given the variability that you mentioned in
movements and the atypical nature of the spring 2013 movement,
that shows a variability that happens. And it requires multiple years
of data collection on caribou to correctly characterize their use of any
one area. And I would question actually whether or not three years is
adequate.
But certainly two years is not. And so I'm really glad to hear
that you're going to do at least a third year.
And one of the recommendations that we would make would
be to try and continue that, to capture the complexity and the
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difference between year-to-year variations and movement patterns,
because it's really going to be necessary in order to evaluate the
impacts of the project on caribou. So that's an observation more than
anything.
The -- and one of the -- another thing is that do you think
there's going to be a difference in impact to the project on caribou
depending on which access route is used?
MR. LAWHEAD: We're not talking about impacts yet. That's
going to be done in the license application.
MR. GILBERT: Yeah. These studies are baseline focused, to
make sure we understand and have the right information in the bigger
study area, to be able to make -- for AEA to be able to make a
proposal, for one, into the impact analysis. So that's down the road.
MS. MCGREGOR: The impacts of each potential road
corridor will be evaluated in the draft license application.
MS. JONES: But again, I think the important point here is that
we are collecting sufficient data to -- to make those assessments
when it comes time to do it with the satellite data and the VHF
telemetry.
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MR. MILLER: One of the -- may I continue? One of the
things is a recommendation more than a comment -- is I think it's
going to be very important, and you're probably already planning this
in your final study report, to document where each VHF and each
GPS collar was deployed and on what sex and age that that was
deployed, because absent information on -- on that, where these
collars were deployed relative to the impact area, is extremely
difficult to determine, you know, whether or not the right animals
were collared.
So I assume that you're planning on doing that for at least your
final. Because there's no way of determining whether or not, you
know, the animals were collared at the right time or in the right
location based on the information that is represented to date.
MS. JONES: Yeah. And I think two points there. One, it's
really exciting that we collared so many bull caribou for this project,
because it's pretty rare actually to put out collars on bulls and get all
this movement data that we're getting off of them. And we're
certainly seeing differences between the bull and the cow
movements, and it'll definitely be something that'll come out in
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the -- in the updated study report.
But another thing is, I've seen so much mixing of the animals,
alternations -- altering strategies and things like that, that I feel pretty
good that we have a good sample of the population collared.
But again, we'll know more when we get into the fine-depth
spatial analysis, but we're certainly keeping all the data on body
condition and age and sex and all of that, yeah.
MR. MILLER: Okay. I just have one more question, with
your indulgence. And that is -- this is Sterling Miller still.
As you are aware, back in the '60s, Ron Skoog did an analysis
of caribou herd structure in this area. And at that time, this
impoundment area was -- proposed impoundment area -- was the
center of the calving grounds for the Nelchina caribou herd, right?
That's right where they calved.
And what happens, would you agree, that what happens with
caribou is that they use large landscapes and they use sort of
traditional portions of that for a period of years, like decades, and
then they shift. And they use a different section of the environment
for calving and wintering, and so forth.
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And so my point generally being is you think that you will be -
- you know, the S&I report for 2011 by the Unit 13 area biologist
mentioned that the Nelchina caribou herd is increasingly using that
area around the Watana impoundment, and I wonder that if this
might be representing a shift in movements from the traditional
calving areas in the foothills of the Talkeetna range, to more impact
to perhaps north to the area where they used to calve, that Skoog
recognized in the '80s -- or I mean, in the '50s and '60s.
And I'm wondering if somehow your studies are going to
capture the fact that the impoundment may well constrain the ability
of caribou to reoccupy these areas of historically important calving
areas, of even the Nelchina River.
MR. SENSIBA: Well, this is Chuck Sensiba.
That's more of an impacts question than a baseline question.
MR. MILLER: What I'm asking is if the data she's collecting
will be sufficient to document whether or not the herd is shifting its
range to -- to occupy more of this historically occupied calving areas
north of the impoundment.
MR. SENSIBA: That's a different question than what I
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originally heard, so I think that's fine.
MS. JONES: Yeah. So the data that we're collecting, we're
going to capture as much annual variation as we can and look to see
if there are any trends.
Certainly caribou do, but we'll also be able to compare our
data to what was done in the '80s and what was done in the '50s.
And so on a really broad scale, we have -- we do have a lot of
data over the variation in these caribou movements. And you know,
one thing I've even noticed is a slight shifting in the '80s, they used
the Lake Louise area a lot in the winter, and they haven't been doing
that for a while, and then this last year they used that area again. So
there's certainly, when it comes time to talk about the impacts and
things, we will certainly dig through the historical data, which is part
of the objectives, and look at what areas they have used in the past
and what areas they might use again in the future.
MR. MILLER: Thank you.
MR. GILBERT: Okay. Good.
MS. MCGREGOR: Appreciate the comments.
MR. GILBERT: Yeah, very nice. But others might have
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some comments before we move on to moose.
MS. LONG: Yes, I do.
MR. GILBERT: Go ahead.
MS. LONG: Okay. This is Becky Long. Can you hear me
okay?
MR. GILBERT: Yes. Certainly.
MS. LONG: Okay. This is a little bit long, but not real long.
These are comments that I'm speaking on behalf of River
Coalition members in Game Management Units 13 and 14. I myself
am a resident of 14B. These are people who have hunted the caribou
of either herd for ten to over 30 years. The words that they have
spoken to me are what the study industry now calls local ecological
knowledge.
The Nelchina herd is a Native subsistence food source for
Copper Basin residents, and we need to bring some of the talks right
down to the boots on the ground. The current movement of the herd
has changed in response to two things: The warm late fall season
and the Tier 1 hunting pressure are the hypotheses of people in the
area and also agency people.
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Usually the herds come down from the high country. They did
not do that this year. The hunting pressure is overwhelming with the
use of ATV vehicles that penetrate further into the remote areas. The
gravel pit at the Susitna River Bridge on the Denali Highway with
mass motor homes, campers, and ATVs.
According to local hunters, the Nelchina caribou herd has
hunting pressure like never before. The seminal area around and
adjacent to both the Denali East and Denali West Corridors has been
characterized as a war zone. Hunters say that the caribou herds are
fractured.
During the previous Tier 2 hunting days, hunters would see
bands of caribou -- bands of caribou, but now they often see just
single caribou, and they look panicked. And I'm bringing all this
up -- I know that we're not supposed to deal with impacts right now.
That's in the draft impact assessment of the license, and I get it. But
we have to make sure that there is sufficient data collected to be able
to recommend to that.
And I just have one more thing. 10.6.4 of the RFP is the data
analysis goal and the project impact evaluation. This is a major goal.
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The evaluation of population and density estimates, delineation of
seasonal ranges and movement corridors will include post-project
habitat loss and detrimental impacts to these herds.
There must be a steady focus on cumulative negative impacts
from all the development actions on these caribou. Specific
developments, there are two of them. One of them is the MMG
mineral exploration drilling project on both state and tentatively
approved state lands east of the Susitna River, and this is within the
10.6 study area.
Now, it is outside the project area, what is considered, but it's
in the 10.6 study area. This is the third year of exploration. 2014
exploratory work at T29 North are by these sections 13, 14, 20, 21,
23, and 24, and T30 North, R60, Section 29.
This is a northern part of the traditional Nelchina herd calving
area. The Talkeetna Mountains calving grounds are considered the
most important single geographic area to the herd. MMG helicopter
flights flew in that area, and also south of the Susitna Bridge on the
Denali Highway towards the headwaters in the Susitna Glacier.
Perhaps some of these helicopter flights were AEA glacier study
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people. The helicopter noises throughout the day, with the usual
high-noise level that permeates the air space, this has to affect the
caribou.
Number two, the JBER Fox 3 impacts of the military operation
areas overflights. The recently finalized environmental impact
statement lays out the future plans for the Fox 3 and the Paxson
MOAs with increased use of the area at lower altitudes and perhaps
pollution from [10:49:50] (indiscernible).
Both projects, coupled with the low building dam construction,
intertie building, et cetera, that will accompany the Susitna Dam
means that the cumulative effect on the Nelchina herd is an issue that
must be looked at this level. Thank you.
MS. MCGREGOR: Thanks for the comments, Becky. Just to
clarify, we are looking at the use of caribou as a subsistence food
source in the subsistence study.
They did do -- complete a set of -- I don't know how many
communities. At least 20 communities have been surveyed over the
last couple of years. They'll talk about that tomorrow. And that did
include the Copper River communities.
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We will evaluate harvest. It is one of the wildlife studies that
we've been deferring. We completed one set of harvest evaluation in
2012, and we're just waiting until the last year of study so we can get
all the additional data that's been gathered on harvest since 2012.
Both harvest, subsistence, and -- well, harvest and subsistence -- will
be incorporated into the impact assessment and the license
application, and we will also address any foreseeable projects in the
cumulative effects analysis.
MR. LAWHEAD: Becky, this is Brian Lawhead. Will you
have -- that information that you just read, will that be in your
comments, so that we can get access to that?
MS. LONG: Yes. I am actually going to file them with FERC
pretty soon, yeah. The traditional -- or local -- whatever it is now. It
used to be TTK, now it's local, blah, blah.
MR. LAWHEAD: Local knowledge. It's good.
MR. GILBERT: Okay. Good.
MS. MCGREGOR: And I just want to say, Becky, we really
appreciate how prepared you are. You provided us with comments
in writing citing specific sections last week, and it's clear that you did
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the same this time. It's very helpful for us. Thank you, Becky.
MR. GILBERT: So are there any other comments on caribou
before we move on to moose?
MR. MILLER: Just one question, and that -- this pertains to
both moose and caribou. And you show your home-range plots, you
know, and you characterize the use as high, medium, and low.
And I'm just wondering if ultimately you're going to put some
numbers on what those categories mean -- high, medium, and low
in terms of density or animal days use or something like that, for
both moose and caribou. Because at the moment, there's no -- there's
no quantitative numbers associated with those characterizations.
MS. JONES: Yeah. And I believe it's in the ISR, and it is not
on -- oh, and it's also on the figure, if you want to bring it up. Those
are 50, 75, and 95 percent utilization contours.
MR. MILLER: So is it reflective of density, the time?
MS. JONES: It's 90 percent of the locations that we have are
within the --
MR. MILLER: Are in the high?
MR. LAWHEAD: 95.
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MS. JONES: 95, sorry. Yes. And it's right there in the --
MR. SCHICK: In the small print.
MR. MILLER: Oh, thank you. I guess I missed that.
MS. JONES: Sorry. No, it's in the key.
MR. GILBERT: Yeah. It's hard to read on the screen.
MR. BURCH: That would be the light green color, that's how
that works?
MS. JONES: Yeah, yeah, 95 is the light green. And then 75,
and then the darkest would be 50 percent.
MR. GILBERT: Well, I think we should keep moving,
because I want to make sure we get to moose and a few others we've
got this morning here before lunch, because those might have
some -- they have a lot of different things to discuss, I think.
Kim, if you can just go through --
MOOSE DISTRIBUTION, ABUNDANCE, MOVEMENTS,
PRODUCTIVITY, AND SURVIVAL (STUDY 10.5)
MS. JONES: Even faster. Okay. All right.
Moose. Objectives are in the ISR. So are the components.
The variance, we've discussed this at length. We weren't able
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to access CIRWG lands. The workaround on this was discussed in
the ISR.
Here's the summary of the collars that we put out. We did
complete deployment of moose collars in March 2013, and then here
are the same contours that we talked, the 50 percent, 75, and
95 percent utilization distribution contours.
And then we've also been conducting twinning and calf
survival studies on moose by looking at them daily during the
calving -- or the twinning period, calving period.
And we also conducted a browse survey in March 2013, and
we've been conducting late-winter surveys to survey the area
surrounding the proposed inundation area to see how many moose
are using that area during the deepest snow part of the year.
We also, in November, conducted a geospatial population
estimator survey, to estimate the number of moose using the greater
project area, as shown here.
And our proposed modifications, we proposed to forego
monthly radio tracking flights of VHF-collared moose in December,
January, February, and April. We weren't seeing a lot of movement
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during that time, and didn’t feel that we needed to do telemetry
flights. But we will be still getting satellite data from those times,
where we get several locations a day.
We are going to conduct another browse survey that's going to
be more focused on the inundation zone and proposed transportation
corridors, and that'll be completed in March 2015, and we will have
access to CIRWG lands. And we'll complete another late-winter
inundation survey in March 2015, as well.
And just like with caribou, we are going to continue telemetry
through May 2015. And to complete the study, we're going to
continue telemetry. The satellite collars on the moose are set to fall
off on November 1, and I'll be going out and retrieving them in the
snow here pretty soon. And we'll continue our count-area surveys
and then the moose browse survey that I mentioned.
MR. GILBERT: Okay. That was really concise. So on
moose, anything?
MS. BULLOCK: Sarah Bullock, BLM.
I assume on the corridors for the focus, you'll be dropping the
Chulitna and adding the east Denali Corridor.
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MS. JONES: We will be using the current corridor maps,
that's correct.
MR. GILBERT: Including reporting any information on the
previous work, too?
MS. BULLOCK: Right.
MR. MILLER: And the study area for these species is much
larger than those corridors, so information should apply.
MS. JONES: The information would apply thus far, yeah.
MR. GILBERT: Mr. Sterling.
MR. MILLER: I would like to congratulate Kim for the
succinctness of her comments. Typically what's done is you use up
all the time so you don't have time for questions.
MS. JONES: No. I'll take questions.
MR. MILLER: Good for you.
MS. JONES: I like input.
MR. LAWHEAD: We encourage succinctness.
MR. MILLER: This is Sterling Miller again.
I'm concerned about the lack of collecting location data on
VHF collars during December through April. And the reason is, is
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that typically the analysis -- now, I understand you're going to
continue to use the GPS collars, but the analysis of utilization data
based on -- is based on the number of point locations in an impact
zone compared to, you know, the number of point locations outside
an impact zone. That's kind of the way it's used.
But if you don't -- and the time that moose are most likely to
occur at lower elevations in the area of where the Watana Dam will
be impacting moose to the largest degree, is in these -- is in winter,
but exactly during the time that you're not going to be collecting data
on the VHF collars.
So your data collection on the VHF collars will be skewed
away from the time when moose are going to be in the area that
would be most impacted by the impoundment, so I'm a little bit
worried about how you're going to deal with that during the data
analysis phase.
MS. JONES: So I guess the moose movements that we're
seeing are around the time of rut, October, November, and then in
December, January, and February they're starting to move down to
lower elevations.
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And then in March, they are typically in the highest snow time
of the year; we will get a location on them, where the animal was at
that time. So we'll know where it was in November and where it was
in March, and we don't usually -- movements that we do see
occurring that time are moving down to lower elevations, and then
we'll see them start moving again in May for green-up.
And so we'll still be spatially covering where the moose are in
the interim, but in getting locations on them during those key times.
So I don't really see that as preventing us from meeting our
study objectives or skewing our analysis.
MR. MILLER: Okay. I think you'll get information on
movement, which is -- I agree, you know, with what you just said.
However, what you won't get is the percentage of the locations of
your VHF-collared moose, which are in the lowest elevations and
closest to the impoundment.
So if you're going to do a chi-square analysis or something like
that, as was -- you know, Warren Ballard did back in the '80s, of the
percent of the point locations that are occurring in the area that will
be most impacted by the proposed impoundment, I don't see how you
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can use the VHF collars.
MS. JONES: So we would be using a number of moose using
the area and not the number of relocations. And so I guess I still
don't -- I don't --
MR. MILLER: That's a much less robust number, because if
you just use the number of moose rather than the percentage of time
that moose are spending in the certain area, proportion of the time,
that's much more typical in a robust way --
MS. JONES: If you're asking about a proportion of time,
we're getting that information through the satellite data, where we're
collecting four locations in a day.
MR. MILLER: So you're not -- that was my question. You're
not going to use the VHF collars to detect -- document the amount of
time that moose are utilizing various impact zones. You're just using
the VHF collars to detect movement data?
MS. JONES: No. I believe we will be using the VHF collars.
And I guess if you would, like, submit some formal comments
about it, on how you think it will impact the analysis, I'll be happy to
look at it when it comes time to review --
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MR. MILLER: We have formal comments prepared, and
that's one. But I was told here to ask questions about --
MS. JONES: Absolutely.
MR. MILLER: And that is a concern, that I think that your
data on utilization on the VHF collars is going to be skewed against
utilization, the time which moose are most utilizing the
impoundment area. That's my concern. And we will submit those
comments.
MS. JONES: And we're also doing the additional surveys in
March, to look at utilization of the proposed impoundment area.
MR. MILLER: And you will certainly get that with your GPS
collars.
MS. JONES: Right, right.
MR. MILLER: And there's no question that that's true. But
I'm concerned about the skew in the VHF collars.
The other thing that I'm concerned about, and I didn't see this
in the -- in the, you know, initial study report, is in your field
sampling -- if you'd go back to slide 8, you can see the Cook Inlet
Regional Corporation land is -- tends to be in the area closest to the
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impoundment in the river.
And so your -- you randomly selected plots, high, medium,
and low plots to do browse utilization surveys, but the bias
associated with not being able to measure browse utilization in the
area that is on the Cook Inlet land, because you weren't able to
document there, I'm concerned about how that bias will be addressed.
Because another way you could address it is there's a lot of
BLM land along Watana Creek there, and you could sort of
oversample. But just because you can't get to the Cook Inlet Region
lands to sample a plot that's high density for -- you know, as you
pre-classify it as a high density strata, doesn't mean that you can just
go and select some other plot and that that's equivalent. You have to
somehow acknowledge and recognize that you're not -- you weren't
able to sample those plots on Cook Inlet land.
MS. JONES: And I agree. And that's why I address this at
length in the ISR, that -- I mean, I can see your concern, and that's
why in the ISR I talked a lot about how many plots were randomly
chosen potentially on CIRWG lands and the method that we used,
how it is all based on finding a landing zone. And I went to a lot of
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detail about this in the ISR.
And also we are going to do -- the initial browse survey was to
get to look at moose utilization of the habitat across the greater
project area, but the upcoming browse survey will be more focused
on the inundation zone, proposed inundation zone, the proposed
transportation corridors, and therefore -- and we do have access to
CIRWG lands for those surveys, so we will be getting at that data.
MR. MILLER: So you're going to oversample in the
upcoming years, those areas that you were not able to get access to
originally, is that right?
MS. JONES: No, we are not going to oversample. We are
still going to use randomized sampling because it would bias us if
we --
MR. MILLER: See, that's my whole point.
MS. JONES: -- do not use random sampling.
MR. MILLER: The fact that you weren't able to get those was
a bias against them, and those are the areas that are likely to be more,
you know, important, in terms of your browse utilization survey.
So unless you do some kind of weighting procedure to select
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good cells that are the ones that you were not able to sample the first
time around, you will have a bias against the high utilization cells.
And so my -- I did read the ISR. I did read your explanation
of how -- of how those would be -- you know, the inability to get it.
And I wasn't convinced that it was adequately addressed, the fact that
you weren't able to get access to all the cells, particularly on the
Cook Inlet lands, on the initial survey. So I didn't think it -- I don't
recall your saying that you were going to be doing more sampling for
browse next year.
MS. JONES: Yes.
MR. MILLER: Did it say in -- if it did, then I missed that.
MS. JONES: Yeah. And they're separate surveys, and that's
why I'm not going to base my sampling of the first year surveys on
the second.
The first year, like I said, was an overview of the entire project
area or the greater -- the whole moose study area, this whole area.
But this next survey will focus more on the proposed inundation zone
and the proposed transportation corridors.
MR. MILLER: So you're saying your analysis on browse
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utilization will not be biased because you aren't going to use the first
year's data in the browse utilization report?
MS. JONES: No, that's not what I'm saying. I'm saying that
there'll be reported -- the results from the two studies will be reported
separately.
MR. MILLER: Right. So the -- the results that are going to be
most interesting are those that are not biased against the Cook Inlet
Regional Corporation lands?
MS. JONES: We will get a lot different information from the
more intense sampling, yes.
MR. LAWHEAD: How many points were you talking about
that you had to show?
MS. JONES: Not very many. I can't remember. It was in the
ISR.
Do you remember how many points were randomly selected?
MS. MCGREGOR: Pull up the ISR, and that screen, they're
all loaded.
MR. LAWHEAD: I can look it up.
MS. JONES: I think it's actually a table in the ISR. It would
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be part -- if it's dated, it's --
UNIDENTIFIED MALE: Part A probably?
MR. LAWHEAD: Section 9, page 9.
MS. JONES: I don't know if it's in the table or --
MR. LAWHEAD: On CIRWG lands, 4 upstream out of 167.
And then the low stratum, downstream is 5 of 168, in the high-
density count.
MS. MCGREGOR: Can you repeat that, so the court
recorder --
MR. LAWHEAD: Okay. It's Table 4.3-1 in the ISR, Part A.
There were 167 -- so there's two study area subdivisions: upstream
high-density stratum had 167 cells, of which four were on CIRWG
lands. The low-density stratum had 156 cells, of which none were on
CIRWG lands. And in the downstream portion of the study area, 168
cells were in the high-density stratum --
MS. JONES: I’m just wondering why it’s not showing up
there.
MR. LAWHEAD: And then in the low-density stratum,
downstream, 147 cells were identified, of which none were on
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CIRWG lands. So it looks like 9 out of 640.
MR. MILLER: On CIRWG lands?
MR. GILBERT: That didn't get sampled, yeah.
MS. JONES: And again, we overselected. We selected twice
as many cells as we thought we would need, knowing that cells
would be passed up based on not having a landing zone, not having
any vegetation, or not having any browse species. So we're not
definitively saying we would have sampled all nine of those, or even
a small portion of them, based on the methods. But it's hard to know
exactly how many we actually skipped over, but it's a smaller
number than shown there, because they would have been --
MR. MILLER: Well, I say I'm just concerned that the analysis
take into account the fact that you weren't able to sample according
to your sampling design, though, cells on Cook Inlet lands in the first
year. That's my point.
Your objective 2 is to assess the relative importance of a
habitat in the inundation zone, proposed access/transmission
corridors, in the riparian area below the project. How are you going
to assess the habitat in your current design with these -- in these
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second two categories, the proposed access/transmission corridors
and the riparian area below the project? You don't have any
radio-collared animals in those areas. Maybe in the
access/transmission corridors you do. I can't tell because I don't
know where you put out collars.
But certainly downstream, the riparian area below, you don't
have anything to assess the importance of the habitat. So you -- is
that just going to be done with the browse surveys?
MS. JONES: So that's actually a good point that you bring up.
The riparian instream flow study is going to be doing a spatially
explicit model in that area, and so they're looking at all the vegetation
that's currently in the area and mapping it, including areas where
willow can be found, which is in a preferred moose browse, and so
they will be entering that into a model, and in the model they'll enter
changes -- potential changes and flow regime, ice -- ice processes,
changes in sediment, things like -- things that might affect how the
seeds and the plants are carried down, all these different things.
And they're doing this in a lot of detail. And they will actually
map changes in that habitat that will occur with the modifications
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that will likely happen with flow.
And so we do have some movement data in that area that we
will incorporate in, after we get the model from them to understand
the changes. But a lot of downstream impacts that are going to
happen are more subtle and they're going to take place over a longer
period of time. And that's why I was -- the fine-scale modeling that
they're doing with the riparian instream flow study is going to be
much more valuable than anything that we can do with current
moose movements.
So I agree that my study alone is not going to meet that
objective, but in combination with the riparian instream flow, and
there's also a riparian vegetation study, and I believe that it'll be
covered sufficiently.
MR. MILLER: I think that's a reasonable answer. It would
have been clarified if you had referenced the fact that this was going
to be done somewhere else, you know, and that would have helped.
MS. JONES: No, I agree.
MR. MILLER: And that is going to be based not on
movements, but rather on inferences from browse availability. So
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that's correct, right?
MS. JONES: Yeah. And I agree, that we do mention working
with other studies, but it could be clarified more in the future.
MR. MILLER: This may have a similar answer, but your
objective 6 is to identify areas for habitat improvement by, quote,
"crushing, prescribed burning, or other habitat enhancements" could
occur, but I don't see any indication in your design that you're going
to be doing any of those kinds of identifications of habitat for
mitigation.
MS. JONES: Yeah. And I actually do have a plan for that
analysis that is more complex, and it's something that's been
proposed to me more recently, something I'm looking into. But it's
called -- and I just totally blanked -- resource selection function.
MR. MILLER: Oh, yeah.
MS. JONES: Yeah. And so --
MR. MILLER: Mark Boyce's technique.
MS. JONES: Right. And so basically with all the data that
we're collecting -- so for each individual, say, moose cow that's out
there, we know her body condition, we captured her, we know
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whether or not she's having -- whether she was pregnant at capture,
and whether or not she's having twins, and the twin survival -- the
survival rate of her calves, and we have all this data collected on this
animal. And we also have all of her movement data. And we also
have the browse data and really good habitat maps, some of it
coming from inside the study.
So basically we can take all of that and we can look at moose
that are foraging in a particular area, if they are more fit than moose
that are foraging in other areas, and that'll help us identify areas of
importance for the moose that may need to be protected or areas of
poor habitat that maybe could potentially be enhanced for the moose.
And so that is my plan for the analysis and the data.
MR. MILLER: As a general point, I would say if you're going
to have objectives, you know, you ought to address those objectives
in your initial study report and say how those objectives are going to
be met.
And so I'm delighted to hear that you have plans on how to
accomplish that, but you can understand the readers' confusion when
you read objectives and no connection to studies that will
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design -- that will provide that information.
MS. JONES: We did have a series of meetings on those
proposed study plans whenever they were written, and so your
feedback would have been great at that time.
MR. MILLER: All right. Well, I'm a hired gun, so -- the other
comment is that in the -- in the Becker–Steigers report early
on -- they actually estimated browse, biomass availability. Are you
going to make any effort to do that actual --
MS. JONES: That's what we'll be doing with the browse
surveys.
MR. MILLER: So you're actually going to estimate browse
availability. Good.
MS. JONES: Yeah. And consumption.
MR. MILLER: Right. Right. Good.
The -- the -- I made the comment about maps showing where
collars were deployed, both GPS and VHS on caribou, and I'd just
make that same comment --
MS. JONES: Okay. And --
MR. MILLER: -- on moose.
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MS. JONES: And I'm not sure how it was when you were
around, but we're very protective of exact locations of caribou and
moose, so we can't give you -- we can't give out the exact collar
locations.
And people own land in the area, and stakeholders wouldn't
want that anyway. But I can give a general idea, maybe a really
large star on the map or something --
MR. MILLER: That's right. Something --
MS. JONES: -- generally where they were put out.
MR. MILLER: -- like that for both -- yeah.
MS. JONES: I can't give out --
MR. MILLER: Fair enough. My wife used to be chief
biometrician for wildlife conservation, as you know, and therefore
we had that same problem with harvest data that exists, and I can
appreciate that, particularly with carnivores. I think less so for
moose, but -- and caribou.
MS. JONES: But yeah. I actually just made the point to
Mark, like last week, that, yeah, we really need to clarify on here
where the collars were put out, because some of these areas where
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we're seeing moose not using the area, yeah, here in these mountains
is because there aren't moose, but other areas it's because we didn't
have a good representation of collars because we were focusing on
the proposed transportation corridors and inundation zone.
MR. MILLER: I noticed in your report, you used terms like
inundation zone in the ISR. However, you know, the map that you
presented showing the inundation zone was much larger than the
actual area that would be flooded. So my suggestion is that you look
for more precise terms of, you know, inundation zone or inundation
impact area or something like that.
MS. JONES: Are you referring to the late-winter survey area?
MR. MILLER: I think that's the map that I saw.
MS. MCGREGOR: So just to clarify, that is the inundation
zone. That's at an elevation of 2,050 feet.
MR. LAWHEAD: The blue.
MS. JONES: But the orange around it, to clarify, does
encompass greater than the proposed inundation zone, yeah.
MR. MILLER: Right. And that is also called --
MS. JONES: The study area.
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MR. MILLER: -- the inundation zone; is that right? She's
asking if the buffer -- the buffer of the future reservoir.
MR. LAWHEAD: We tried to standardize terminology to
state a buffer size around the inundation zone.
MR. MILLER: Okay. Well, it wasn't clear to me, so I just
suggest you be a little more clear on that.
MS. JONES: Sorry.
MR. MILLER: So how are you going to estimate population
size, which is one of your objectives, and determine what area to
which that population size will apply? I understand that -- I read
about your surveys and so forth, but I didn't actually see a technique
for estimating, you know, your regular survey, inventory surveys,
and so forth, whatever you're doing. But I didn't see a mention to a
Gasaway technique or something like that, but --
MS. JONES: The geospatial population estimation survey in
November is a modified Gasaway. It's been updated slightly, and
this is the population estimate and the density that was derived from
that survey.
MR. MILLER: Was that in the report, ISR?
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MS. JONES: The -- it was just -- the method was discussed,
but these results are since the ISR. The data compilation was since
the ISR.
MR. MILLER: So in this whole area, you have 3,600 moose
with the -- with the variation indicated --
MS. JONES: Uh-huh.
MR. MILLER: -- is that right? In that whole area surrounded
by the blue?
MS. JONES: Purple, yeah.
MR. MILLER: Or the purple?
MS. JONES: Yeah.
MR. MILLER: And so is that going to be somehow reduced
to -- spatially to something that is reflective of impact zones, you
know, further away from the impacts, this is how many moose there
are, and close to the impact -- to the impoundment area, this is how
many moose there are? Is there going to be some way of coming up
with a number of moose which will be more directly affected by the
impact?
MS. JONES: You know, we can certainly do that using the
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density.
MR. MILLER: All right. So you will do that?
MS. JONES: Yeah.
MR. MILLER: All right. Well, thank you very much.
MS. JONES: Yeah, yeah.
MR. LAWHEAD: Plus she did specific surveys of the
inundation zone.
MS. JONES: Right. Which is the area from the '80s that was
highlighted as the most concern, was the inundation zone. That's
why we're doing those March surveys. And AEA has allowed us to
do an additional March inundation survey because we counted the
exact same number of moose in two different years, and we'll want a
third year to get more variation.
MR. MILLER: I just noticed that, as I did with caribou, that
Ballard and Whitman spent a great deal of effort in their studies in
the early '80s identifying moose subherds and describing their
patterns of movement, and so forth.
And I didn't see -- and you know, he -- and he also described
the kinds of impacts and their magnitude that would occur for each
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of the subherds, you know, some of the herds like the Watana
subherd and so forth will be very greatly impacted by many things,
doing inundation on the browse, and so forth, and there are different
ones would be impacted in other ways less [11:20:18]
(indiscernible). Are you going to do something like that?
MS. JONES: I'll certainly see if any particular strategies like
that show up in my spatial analysis. And if they do, I will certainly
highlight them and discuss impacts separately when it comes time.
MR. MILLER: For subherds?
MS. JONES: If I do believe there are subherds, yeah.
MR. MILLER: So you don't believe that Ballard was correct
in identifying those subherds?
MS. JONES: Well, I'm just saying if my data doesn't show
specific subherds, I'm not going to comment on them. His study area
was also much larger than mine, and so I was focusing all of
my -- I'm focusing all of my efforts on animals that are in close.
So I believe I have his map with me, and I believe that only
covers what he called two different subherds, but I'll certainly look at
it.
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MR. MILLER: All right. Thank you.
MR. LAWHEAD: And that was based on VHF telemetry?
MR. MILLER: Yes.
MR. LAWHEAD: It's a benefit of GPS collars.
MS. JONES: Right. Now we have -- right.
MR. MILLER: There's no question that the GPS is a huge
step forward from what was available in the '80s, and I congratulate
the Energy Authority for springing for the GPS collars because that's
a significant advance in your ability to collect resolution on habitat
utilization.
I just wanted to emphasize that I decided as a time-saving
mechanism to only emphasize concern and not say good things.
MR. GILBERT: Well, you can say good things, especially
when you concur.
MR. LAWHEAD: Kim can use some good comments.
MR. GILBERT: Yeah. That's great. That was great dialogue
there.
MS. JONES: Yeah, thank you.
MR. GILBERT: Very good.
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And I do want to kind of keep moving, but if somebody's got a
burning question on the phone, please go ahead.
MR. WOOD: This is Mike Wood. Can you hear me?
MR. GILBERT: Sure, Mike.
MR. WOOD: Yeah. Hello. I’ve been listening to the caribou
use, and I would just like to interject that regarding the lower riparian
studies, I -- an emphasis on other people collecting that data perhaps.
Again, I'd like to flag, for FERC, the winter -- amount of
winter effort and the effects of what the proposed dam could have
below the dam site, especially with ice creation, jamming, and spring
jamming, which creates -- just scours these islands creating the
willow browse that the moose use throughout the entire winter in
2012, when they were -- when R2 was doing their initial studies out
here on the river, in March, I helped put a trail in.
I could count from my house, which is right across from the
Whiskers Slough focus area down to the confluence, 47 moose on
the river utilizing the overflow and the browse to eat from. Within a
week, all those moose had disappeared because of the traffic and the
study efforts, and they weren't to be seen again.
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In 2013/14, I witnessed the same thing. There was quite a few
moose until the -- until the helicopters and snow machines started
flying around.
I guess my -- my point is, I haven't actually seen people down
here studying the number of moose on the ground between October,
November, December, February, March, and in April, and I -- it's
important, because I think we're assuming the effects of the dam will
be minimal down below -- downriver.
Again, that's an assumption if there's no ice jamming, there's
no browse being created by scouring the islands. And if there are
higher flows, it might be difficult for moose to actually hang out on
the river itself with higher water levels.
So I think that in my mind, a very important thing to see,
especially the impacts of the studies on the local animals here. And I
also just want to interject, as far as the caribou go, I've seen a
massive change in their habits in the last couple of years, and then
descending way low, incurring down into the line and whatnot in
greater numbers of caribou.
There's over -- I just think the efforts on moose should be
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greater in the impacts of what could happen to their habitat with
higher water, no ice jamming, and how many moose are actually
descending from the higher elevations to this river corridor between
Portage and the confluence of the Chulitna, Talkeetna, and Susitna
River.
Thank you.
MR. GILBERT: Okay. Thanks.
MS. LONG: This is Becky Long again. I have one more thing
I forgot to add with the caribou.
But when she was talking about the anomalous spring in 2013,
because the calving and the migration route were changed and all the
patterns change, because of the late break-up and blah, blah, blah,
and then the rivers were open, there was significant calf mortality,
drowning, from being not on their usual calving areas and having to
cross rivers. So I think that should be in the public record. It's pretty
important.
MR. WOOD: And this is Mike again, Mike Wood. I'd just
like to add that during spring break-up when there is shelf ice and the
river is flowing prior to the flood -- the spring flush coming through,
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we'll have herds of 12 to 15 to 20 moose going up and down the side
of the river right in front of our house, wading actually across
because they find that shelf ice and the [11:26:06] combination
(indiscernible - interference with speaker-phone) for going across.
So they actually herd up and travel up and down the sides of the river
until they can actually cross that river. Thank you.
MS. JONES: I just wanted to clarify really quickly that the
drowning we saw in the calves were in the Copper River, not the
Susitna River.
MS. LONG: No, no. It wasn't in the Susitna River. But it's
just --
MS. JONES: Okay. I just wanted to note that.
MS. LONG: No. And I'm sorry I didn't specify. And I can't
remember the exact article. It was in the newspaper over there. It's
just noting that there was some impact on the population because of
the anomalous weather conditions.
MS. JONES: Right. And they did really well this year, calf
survival and production were really high and the calves were some of
the biggest we've weighed in a long time -- that we weighed last
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week. So the herd is -- thankfully seemed to bounce back from that.
But it is good to know.
MR. MILLER: Just one more brief comment from Sterling
Miller.
I didn't see any winter severity index or anything like that in
the ISR. And you know Ballard, when he did his studies, he
developed a winter severity index so you could characterize how
typical or atypical of conditions that the animals were in. And this
pertains both to moose and caribou.
So I would think in the final report, it's going to be necessary
for the years of your study to find some ways of characterizing
whether the years you studied were anomalous or typical. And like
winter severity index is one of those ways.
MS. JONES: Okay.
MR. GILBERT: Okay. Thanks. I think we should move right
into Dall sheep, which is a tag team with you two guys.
MS. JONES: I might let Brian do it.
MS. WOLFF: This is Whitney. Could I ask one quick
question, just about the continuation of the moose browse survey?
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MR. GILBERT: Okay.
MS. WOLFF: Is that going to go on -- I know the [11:28:02]
[telemetry] data from the -- the actual animals, it's going to go just
through May of 2015. What's the timeline of the continuation of the
moose browse study?
MS. JONES: It will be conducted at some point in
March 2015.
MS. WOLFF: Is there something more specific or -- can you
give me a broader timeline than sometime?
MS. MCGREGOR: March 2015.
MS. JONES: Sometime in the month of March 2015.
MS. WOLFF: Okay. And what's the duration and --
MS. JONES: It's typically about a five-day survey, but it all
depends on weather. We have to have good weather for the
helicopters to be able to fly and pilot availability, and all the other
logistics that we work around.
MS. WOLFF: Okay. And then do we know the random plots
for that -- I know you and Sterling had that long discussion on which
ones you'd be, you know, using, and is there somewhere we can view
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what you -- the determined plots?
MS. JONES: No. Sorry, that's not available at this time.
MS. WOLFF: Okay. All right. Thanks.
MR. GILBERT: Okay.
MS. MCGREGOR: I'd just like to ask that we really rapidly
move through these presentations and allow a good time for the
discussion, because we really appreciate the comments.
MR. GILBERT: Yeah. The comments are the highlight. You
did great on these. That was quick on moose.
MS. JONES: A little faster?
MS. MCGREGOR: (Indiscernible.)[11:29:38]
MR. GILBERT: Try to match that. That was about three
minutes.
DALL'S SHEEP DISTRIBUTION AND ABUNDANCE
(STUDY 10.7)
MR. LAWHEAD: Okay. Dall’s sheep. Pretty
straightforward study looking at estimated population size in the
study area, delineating summer range at the same time of those
surveys, those aerial surveys, and then the second component is to
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look at mineral licks in the area. And a third component was to
relate the currently collected data to historically collected data.
Again, there's three primary components, aerial surveys in
current years, mineral lick surveys in current years, and then
comparison with historical data.
There are two mineral licks that were studied in the '80s and
have been revisited in 2013 and also 2014. One is on Jay Creek. It
would be located above where -- above the maximum pool level of
the inundation zone, but fairly nearby.
So in each of 2013 and 2014, we paid two visits in late May
and mid-June and conducted observations at the lick and then -- at
the licks -- and then also deployed a time-lapse camera to record
sheep at the lick between the two visits.
This shows the subdivision of the area, in terms of -- in terms
of subpopulations of sheep in the area. This is the Chulitna
Mountains area, the Watana Creek hills area, and the West Kosina
hills area. And the two licks are located here.
Oh, oh. Here we go. So Fish & Game was able to conduct
aerial surveys of those three areas in July 2013, observing 512 sheep.
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And most relevant to this project in the -- in the lick areas in the
reservation -- reservoir inundation zone is that about 41 of those were
in the Watana Creek hills. Not many sheep were seen at the licks.
About a maximum of seven at Jay Creek and three at Watana Creek,
although that was a fairly brief visit at Watana Creek.
The sheep population in this area declined pretty sharply about
15 years ago, and they've remained low since then.
This page just shows locations of the sheep that were observed
on the surveys in July of 2013. And this is a photo of the Jay Creek
lick site and kind of just a simple little line graph of the number of
sheep seen in that period between the late May and the solstice.
Again, we repeated the general lick visits in 2014. Nine sheep
were seen around the Watana Creek lick; they weren't all at the lick.
But no sheep were seen at Jay Creek. And not many sheep were
present on the time-lapse photos this year at Jay Creek. Maximum at
one time was only three.
No modifications are anticipated.
The main problem this year was that the weather in 2014 was
unusually cool, and so the snow persisted at high elevations and
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didn't allow sheep surveys to be conducted as planned. So that
survey's been kicked into next year, the second year of the sheep
aerial surveys. But no further work on mineral licks is contemplated.
And again, the only field component remaining is the
second-year aerial surveys, and then preparation of the report.
MR. GILBERT: Okay. That was pretty good, both of you.
How about Dall’s sheep? Sterling?
MR. MILLER: I have almost no comments, you'll be
delighted to hear, because I thought this -- this project built well on
the earlier studies and expanded them in very appropriate ways. So
I'm violating my principle of making only negative comments.
But I do have a suggestion, that I think if you go back to your
slide 2 or 3 which showed the populations of sheep, and you'll notice
that your population in the West Kosina hills and the population, you
know, the Watana population, around opposite sides of the proposed
impoundment, and I'm wondering why you don't -- haven't proposed
some studies to determine how isolated those populations currently
are from each other. Because it's clear that the impoundment will
isolate those populations even more severely than they are currently
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by the Susitna River.
And my suggestion is that this be done with genetic studies.
As you know, you can -- you can document amount of interchange
between populations of animals by analyzing, you know, the roots of
hair for genetic composition. It's a fairly standard technique, and I
don't even think you'd have to capture the sheep to do it. You could
probably pick up hair tufts and analyze them genetically.
Because I think if the impoundment is built and there is any
interchange between those two populations, that interchange will be
eliminated.
MR. LAWHEAD: Okay. Thanks for the comment.
MR. MILLER: Do you think there's movement between
them?
MR. LAWHEAD: I'm not aware of any data to suggest that.
MR. MILLER: Neither am I.
MR. LAWHEAD: There was one -- one of our raptor crews
saw a sheep down on a cliff down by the Susitna, down near the dam
site. That's a population of one that's not shown.
But clearly, you know, there are occasionally movements
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outside of well-defined areas of habitat.
MR. MILLER: Are there any licks in the West Kosina hills?
MR. LAWHEAD: Not that I'm aware of, but we haven't
searched for that.
MR. MILLER: I'm not either. So it's not unreasonable to
suspect that perhaps the sheep in the West Kosina hills might be
attracted to north of the river.
MR. LAWHEAD: It's possible. All the movement that we
saw at the Jay Creek lick was to the north, movement of animals
coming and going, even in the same day. It was interesting. There's
some pretty dangerous habitat from the standpoint of large
mammalian predators.
MR. MILLER: But problems of population isolation and
small populations of ungulates is a serious problem and things that
contribute to that isolation are matters of concern, you would agree,
Brian?
MR. LAWHEAD: Uh-huh, sure.
MR. GILBERT: How about on the phone? Any other
technical agencies, otherwise? State? Other questions?
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MS. MCGREGOR: As we move forward through the
presentations, so we can make sure that we have adequate time for
discussion, let's just assume that everybody has read the ISR and skip
over the objectives and study components and just move on to the
summary results and proposed modifications.
MR. GILBERT: Just go to results and modifications? And we
can go back --
MS. MCGREGOR: Well, variances, too.
MR. GILBERT: Yeah, variances --
MS. MCGREGOR: And only discuss significant variances.
They are all fully explained in the ISR.
MR. GILBERT: Okay. So we're going to do wolverine next?
MR. LAWHEAD: Sure.
MR. GILBERT: Mark Burch will do the wolverine study.
MR. LAWHEAD: Are you on the phone, Alex?
MR. PRICHARD: Yes, I am.
MR. LAWHEAD: Okay.
Alex is on the phone, too, Mark.
WOLVERINE DISTRIBUTION, ABUNDANCE, AND
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HABITAT OCCUPANCY (STUDY 10.9)
MR. BURCH: I'll try and build on Kim's success and go a
little quicker through here.
There are the objectives. There's the components.
The plan spelled out in the study plan, as the component
suggests, is to complete a SUPE survey as well as occupancy
modeling, to do the SUPE hopefully at least one time, and occupancy
modeling surveys annually, or twice in this case with a two-year
study.
We conducted the occupancy flights in 2013, and those are
indicated by the dark pink, if you want to call it that, survey areas.
Wolverine were detected in 23 of those 25 sample units.
Sorry about that.
There are no modifications to the FERC-approved study plan.
We were not able to complete the occupancy modeling or the SUPE
in 2014. They both require pretty specific snow conditions and
weather conditions following the snow event. And so it's necessary
for us to conduct that work in 2015.
Once again, if the conditions don't develop for the SUPE, then
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we hope to at least be able to do the occupancy modeling.
UNIDENTIFIED FEMALE: (Indiscernible - interference with
speaker-phone.) [11:39:50]
MR. LAWHEAD: Could you please mute your phone if
you're moving furniture?
MR. BURCH: So once again, that's the plan for 2015 is to do
the SUPE, and if that doesn't work out, at least the occupancy survey
work.
MR. GILBERT: Very fast. Please, Sterling.
MR. MILLER: Sterling Miller once again.
I want to start off by acknowledging that there's probably no
more difficult creature to work on than wolverine, and so everything
I say is in that context, that I acknowledge that.
And -- however, you have two objectives, objectives 3 and
objective 4, which are to describe habitat use in both cases in late
winter, and -- but the only thing I could see in your objectives -- I'm
trying to look for a match between objectives and study plan. The
only thing I see is some population estimation objectives and some
occupancy modeling objective. I don't see any objective for
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determining habitat use. Are you considering habitat use to be
synonymous with occupancy?
MR. BURCH: I wouldn't say so, but we do expect -- assuming
we're able to complete SUPE, we would -- you may be familiar with
that process where -- for the sake of everybody else, I'll explain it
really quickly -- that you use the sampling grid that was up there, and
then once you cross the track you follow it to where the track first
appears, which would be -- presumably be -- the end of the snow
event, and then follow it the other way until you either find it going
into a hole or until you find the animal.
And so we have a pretty good idea of the habitats that that
animal crossed, at least during that time. And so we get some
indication of habitat use that way.
MR. MILLER: So somehow you're going to plot that GPS
track of that track that you're following from the airplane,
superimpose that on some kind of habitat map and evaluate habitat
use in that way?
MR. BURCH: Right. That would be my understanding of the
indication that we would have for --
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MR. MILLER: So I don't see any -- any analysis like that
either in the study plan or anywhere else. So you know, that's a
perfectly reasonable way of doing it, but I don't see it described.
And that is an appropriate way to describe habitat use in late
winter, but you need to say that that's what you're doing. And if
you're not going to do it, don't say that you're going to describe
habitat use and -- if you're just going to do occupancy and
abundance, because that's all I really saw.
MS. MCGREGOR: And, again, I just would like to clarify for
you that there is another study, I'm not sure if you're familiar with,
that is a complete vegetation mapping study for the purposes of
wildlife habitat.
MR. MILLER: I am aware of that. And you mentioned it
before.
MS. MCGREGOR: Okay.
MR. MILLER: And I'm --
MR. LAWHEAD: But that's only within two miles of the
corridors. That's not the entire wolverine study area, so that would
have to be a different land-cover map and use.
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MS. MCGREGOR: Right. To the level of data that we have.
I think we initially started off with a AVC Level III, we have AVC
Level III data at least in that study area, and so it's really the Level
IV that's part of the vegetation --
MR. SCHICK: We're mapping to Level IV, but we'll
aggregate -- this is Terry Schick from ABR. We'll map to Level IV,
aggregate to broader scale wildlife habitats within that two-mile
buffer.
For wolverine, you're going to want to expand that. We'll have
to crosswalk those data with a more coarse-scale habitat map. There
are a number of maps available that you could do that with now. It's
all do-able.
MR. MILLER: It's do-able. And I'm just -- I'm commenting
on the disconnect between the stated objectives and the stated
techniques for the project. And if there's not a disconnect because
some other project is going to do that, then that disconnect doesn't
exist. But otherwise, it does.
The other thing that I was going to wonder, I didn't see any
indication of a -- I said you have a trend index as one of your
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objectives, but I saw no indication of the scale for that trend index.
Is that going to be on a scale that's appropriate to the project or a
subunit, game management subunit or game management unit scale?
I don't know what scale this trend indicator is going to be.
MR. BURCH: The idea would be to use the occupancy
surveys over time as that index. So they would need to be completed
in a similar fashion to how they're being completed in this study for
that particular area, and then you'd have to decide to what extent
could you extrapolate.
MR. MILLER: So the occupancy surveys are going to be the
trend indicator?
MR. BURCH: Right.
MR. MILLER: And is that -- at what scale is that -- do you
think that those are going to be significant? I'm working into my
second part of my question, was whether there were going to be any
power analyses conducted, either for the population estimation value
or for the trend index, and whether we're going to have an indication
of power, which for the purpose of others I will mention is your
ability to detect a change with a certain level of probability. That's
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called a power analysis.
MR. BURCH: Our focus at this point is on the study area, so I
hate to speculate beyond that, what that occupancy modeling could
be used for.
As far as the analysis, I know that Alex is on the phone.
Unfortunately, we've lost the principal investigator for this particular
project from Fish & Game, and so we're at a point now where we're
in the process of doing some hiring and consulting with others to
answer that particular question.
There's -- there was some debate during the development of
some of the reports on what level of change we could detect, and I
guess I'll leave it at that rather than get too far out on my
biometrics --
MR. MILLER: Limb?
MR. BURCH: -- limb. And I'll say that's something we're
working on.
MR. MILLER: Good. I mean, you've got an expert in Region
2 with Howard Golden. And I don't know why he can't be your -- I
didn't realize you had a vacancy, but Howard is certainly an expert.
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MR. BURCH: Right.
MR. MILLER: My last point is that most of the studies, I
think, all except this one, had an objective of incorporating previous
studies into your final report, but the wolverine study did not state
that objective. The earlier studies which Whitman and Ballard, 1984,
they put out 22 radio collars on wolverine, and certainly integrating
those results into your final study report should be an objective for
the wolverine studies.
And that concludes my comments. Thank you very much.
MS. MCGREGOR: Thanks, Sterling.
MR. GILBERT: Thanks, Sterling.
How about other comments on the wolverine study for Mark
and others?
MS. WOLFF: Whitney, I had a hard time hearing Betsy’s
response on, like, habitat-use studies she referenced. I couldn't hear
her at all.
MR. GILBERT: She was talking about the other mapping
studies.
MS. MCGREGOR: I was just trying to clarify -- I think it's
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kind of difficult that an observation I've been making, we have new
people contributing and providing comments on these studies, and
some of the information is being gathered in other studies, and it's
just not really clear to people.
So I was just trying to clarify that we do have habitat maps in
various -- you know, various levels of refinement, and then there is
the wildlife habitat mapping study which will go down to the AVC
Level IV.
But as Brian pointed out, that only covers about a two-mile
buffer around the project area, as defined by the reservoir inundation
zone and the corridors.
MR. GILBERT: And we'll talk more about mapping in the
afternoon.
MS. MCGREGOR: Yeah.
MS. WOLFF: Thanks for repeating that. I don't know why it
is, but Betsy's really hard to hear.
MS. MCGREGOR: I'm surprised.
MR. GILBERT: Yeah. Okay. So, Rick Merizon has joined
us to talk about the ptarmigan study.
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POPULATION ECOLOGY OF WILLOW PTARMIGAN IN
GAME MANAGEMENT UNIT 13 (STUDY 10.17)
MR. MERIZON: Yeah. Just for those on the phone, again,
this is Rick Merizon. I'm with Fish & Game, and I'll be reporting on
the ptarmigan project.
Zip right through the objectives here and get right to the
variances. We have several I wanted to report on.
The one that you've been hearing about all morning, and I'm
sure we'll continue to hear about in the afternoon, is the -- the spring
and summer of 2013. It's certainly affected our project, and
primarily affected our ability to access several of our proposed
capture locations. We were not able to get to the site we call Upper
Fog Lakes or Jay Creek.
And as a result, we were also not able to put out as many radio
collars because of late access to these capture locations and
subsequent difficulties in moving around each capture location when
we were there. And then we also added the Denali Highway capture
location just to the east of the proposed -- one of the proposed access
corridors.
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Another variance was relative to our capture methods. We
were trying to identify the most effective capture methods to boost
our capture rate. And the net gun and noose carpets were in
the -- outlined in the RSP, the study plan. The one method that we
incorporated after the fact was the use of mist nets, and we did find
that this was a very effective technique, particularly for the late
summer captures.
And finally, the aerial transect flights, we were not able to
complete the March 2013 flight but did complete -- we moved it to
the winter of 2013/2014 and did complete two flights, one in January
of 2014 and one in March of 2014. And let me just double-check to
make sure --
Moving to the results, as far as our number of radio collars that
we did deploy, again, as I stated earlier, in 2013, we did not -- we
were unable to access as many locations as we wanted to, and when
we were there, we had difficulty moving around on foot to capture
birds. And so subsequently, we were not able to put out as many
radio collars in our May and August efforts of 2013.
But we did improve that considerably this spring and late
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summer, and we were also able to access several other locations that
we had originally proposed.
Our aerial transect surveys were interesting. We did not get
the flushing rates that we were anticipating in both our January 2014
or our March 2014 flights. And as a result, we -- at the April 2014
meeting, AEA agreed to cancel that effort as we were just unable to
get the flushing rates that we needed to have the detection
probabilities that we needed to make an inference.
Proposed modifications -- let me just double-check here in my
notes. We -- as I said, in 2013, we were only able to access Busch
Creek and the Denali Highway areas, but in 2014, we were able to
access the Denali Highway, Busch Creek, Butte Creek, and Deadman
Lake and Upper Fog Lakes, and we plan to revisit those in 2015.
For proposed modifications, we hope to continue our capturing
and collaring efforts in May and August of 2015. We also hope to
capture and re-collar previously collared birds, again, in May and
August of 2015, and that will allow us to reach our collaring
objectives within each year.
How we propose to complete that, again, we are hoping to
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reallocate the funds that were originally allocated for the aerial
transect surveys to our radio telemetry surveys, which will certainly
increase our ability to make inferences relative to bird movement and
habitat use.
Again, we hope to capture and collar additional birds in May
and August of 2015, and again, recapture and re-collar currently
collared birds also during that time period.
If you have any questions?
MR. GILBERT: Very good. So a variety of activity and shifts
in your time.
How about on this study, you guys? Agencies have --
MS. BULLOCK: This is Sarah Bullock with BLM.
I just want to make sure I understand it. So the ones that
you've gotten -- I didn't see a whole lot in the Chulitna corridor. But
the Gold Creek area, and then there's been I think the Denali and then
the -- I guess Deadman Lakes was the only ones that are kind of
close to the corridors.
And I was just kind of curious. Are you using -- when you
found the habitat type, you're going to use that in the habitat study
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that will be done in 2015, to kind of extrapolate where they're going
to most likely occur in their population and whatnot?
MR. MERIZON: We -- there's very little historical
information relative to Willow Ptarmigan in this particular area. So
the capture locations are fairly insignificant in terms of the specific
location.
Really we are just trying to find areas that we could access
relative to proposed study areas and corridors that we could then
evaluate the overall extent of movement and habitat use, because
really there was no historical information there.
So we weren't certain where the -- whether those birds were
going to have very limited movements relative to a capture location
or very extensive movements, and what we're finding through just a
very basic results for aerial telemetry observation points is that it's
sort of a mix of the two.
So I'm not sure if that's addressing your question or not.
MS. BULLOCK: Let me think about it.
MR. SCHICK: Well, this is Terry Schick with ABR.
We will be doing a wildlife habitat evaluation.
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MS. BULLOCK: Right. I was just kind of wondering if this
was going to be, again, to try to look at the -- you know, you said
some habitat values, and is that going to be kind of put on
that -- those different corridors to try to tell --
MR. SCHICK: Yes. For birds, we'll talk about this this
afternoon. But we're going to evaluate categorical rankings for
habitat value for all bird species that have been recorded in that area.
So Willow Ptarmigan will fall into that group. So yes, there
eventually should be a map that can be produced that'll display high,
low, medium value habitat for Willow Ptarmigan.
MS. BULLOCK: Yeah. I just want to make sure I kind of
understood that that would be in that --
MR. SCHICK: Again, that's going to be within that two-mile
buffer mapping area. It's based upon the detailed map being
prepared in Study 11.5.
MR. GILBERT: Are you guys able to hear on the phone
okay?
MS. LONG: Yeah. It sounds good.
MR. GILBERT: Okay. Good questions.
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How about any other questions for Rick and his study of
ptarmigan?
Okay. We have one more study and then we get to take a
lunch break.
MR. LAWHEAD: Yeah. We need to push through this. Are
Casey and/or Laura on the phone, I hope?
MS. PRUGH: Yes, both of us are here.
MR. LAWHEAD: Okay. And you have a commitment at
1:00, right, Laura? So we should push through this.
MS. PRUGH: Yeah.
MR. LAWHEAD: And then I'll call Nate, who's up after
lunch, and tell him it might be a little bit delayed, because he's in the
field. I hope I can get ahold of him.
TERRESTRIAL FURBEARER ABUNDANCE AND HABITAT
USE (STUDY 10.10)
MR. LAWHEAD: Okay. So just a brief introduction, this
Study 10.10, Terrestrial Furbearer Abundance and Habitat Use, is
being done by the Institute of Arctic Biology at the University of
Alaska Fairbanks. Laura is a professor there and Casey is a grad
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student. And with that, I will let you take it away.
I don't know if you've been listening so far very much.
MS. PRUGH: Yeah.
MR. LAWHEAD: But we need to clip through the -- clip
through the slides at a brisk pace.
MR. GILBERT: Yeah. Focus mostly on the significant
variances and plans to complete the study, any modifications, and so
on, that's of importance.
MS. PRUGH: Okay. Sure. And I'm going to go through the
first half and Casey will take up the last half.
Okay. So our objective is to estimate population size of the
smaller furbearers and their prey and look at habitat use.
And, Brian, are you advancing the slides?
MR. LAWHEAD: I am. And there'll be a little bit of a delay,
so tell me before you want me to turn it.
MS. PRUGH: Okay. Sure. Go ahead.
Okay. So the study consists mainly of collecting scat and hair
samples for fecal genotyping to develop population estimates for
each species.
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We also conduct aerial track surveys each winter, and we'll do
some occupancy modeling.
Okay. Okay. You can advance.
So the lack of access has been probably the main issue causing
variances with our study, especially for marten. So we did not have
access to lands that we had originally planned to work in, and so we
expanded our area into -- into some other areas to make up for that.
We also had some issues with the lynx hair snags not working
out as well as we had hoped. And we slightly modified the prey
sampling to get better spatial coverage for snowshoe hares and voles.
Okay.
So in 2013, we -- Casey and his assistant collected 131 scats
and 29 hair samples.
All right.
And in the prey surveys, there were 15 areas where hare
pellets were counted and where voles were surveyed. Densities were
highly variable, but overall densities were fairly low for both hares
and voles.
Okay.
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And we conducted three aerial track surveys in the winter of
2013, and this figure shows just a summary of the number -- total
number of tracks seen for lynx, marten, and fox, as you move east to
west along the Susitna. And there were no coyote tracks in winter of
2013.
All right.
MR. POZZANGHERA: Okay. This is Casey. I'll take over
here.
This past winter, 2014, we continued on with our scat and hair
collections. We had almost double the hair sample collections and
an additional hundred -- hundred or more scat samples. Part of this
is probably due to the fact that there was less snow, easier to see
samples.
Okay. Go ahead.
The summer prey surveys were conducted in July this summer.
We continued to have pretty variable hare densities, but we saw a
huge increase in vole captures, as you can see between the
'13 -- from the 2013 summer season. And we had 87 captures this
year.
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Go ahead.
The aerial track surveys that Laura was able to conduct this
year were fairly limited, due to the strange and varied snow
conditions. Pretty much the two that were able to be done followed
along the same procedures as 2013 surveys, and she was able to
detect some coyote tracks this year, which as she mentioned we were
unable to detect in 2013. Also probably a product of the lower snow
conditions, predators were able to move around a little easier.
And as far as the genetic analysis goes for the 2014 samples,
well, we've completed all 2013 genetic analyses for the scat samples
and we are working our way through the 2014 samples. As soon as
those are done, we'll be able to continue with some preliminary
population estimates for the coyote and foxes, and the occupancy
modeling using the 2014 track data is under way right now.
Original proposed modifications in the ISR, the major
variances were those that we touched on briefly at the beginning,
consisting of the modifications of the prey surveys and the lynx
surveys. Those were continued during 2014; however, we did drop
the use of the motion-sensing cameras. We didn't find they were an
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efficient use of sampling time, and we had low detection probability
using those cameras.
We did plan on including the marten surveys as we had
originally laid out during the 2014 season; however, we were still
restricted in the areas that we could sample during our 2014 season.
We still hadn't acquired access to CIRWG lands, so we -- we
sampled an area of suitable -- what we decided was suitable -- habitat
and a representative habitat based on cover type. And that was north
of the reservoir area and still a similar size to what we had originally
laid out.
We were able to access a little bit deeper near the study area,
especially down in the Deadman Creek corridor toward the proposed
dam site, thanks to a change in our base camp locations, and we are
planning on using all the data we've collected in the last two winters
in the areas that we've had accessible to us, and extrapolating across
the entire study area based on using habitat characteristics.
The newest modifications since the last edition of the ISR was
that the Chulitna Corridor was dropped from the study area. We've
also -- we were able to increase our hair -- our lynx hair samples
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dramatically this year by implementing a backtracking protocol,
which basically consisted of two field technicians, myself and
another tech, periodically and opportunistically backtracking fresh
lynx tracks through dense cover and collecting hair samples off of
natural rub locations.
We were also collecting incidental wolverine and wolf sign,
whether that be just track -- noting track locations -- or collecting
scat and hair.
In order to complete the study, we basically are done with the
field work, so this 2014 winter and 2014 summer field seasons were
our last. We have worked our way through the majority of our scat
samples and have completed the extraction phase.
We still need to amplify and produce individual fingerprinting
in order to get the population density estimates. And our occupancy
modeling is under way right now, and we're hoping to complete that
here in the next few months.
MS. PRUGH: All right. So I think that's pretty much it.
Ready for questions.
MR. LAWHEAD: Thank you, you guys.
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MR. GILBERT: Yeah, great. That's a great summary.
Interesting study.
What do we have for comments, modifications.
You guys on the phone have anything?
MR. LAWHEAD: There's an advantage to going at
lunchtime, I guess.
MR. GILBERT: Yeah. It's right before lunch, I guess.
Well, it sounds like you made good progress adjusting to the
season, so that study sounds good.
MR. LAWHEAD: All right.
MR. GILBERT: Well, we're going to break. Thank you very
much for your time there. We'll break and, you know, I think we
should just do a full hour, so maybe we'll just start --
MS. MCGREGOR: I think we should come back at 1:00.
MR. GILBERT: Okay.
MS. MCGREGOR: I don't know how many more
comments --
MR. MILLER: I have a great deal on large carnivores.
MS. MCGREGOR: Yeah. So let's come back at 1:00.
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MR. GILBERT: So let's get back at 1:00. So let's break right
now and we'll try to start up right at 1:00, if we can.
(Off record.)
MR. GILBERT: Okay. Let's start up again. We have a lot to
cover, and there may be a lot of comments and discussion, so quite a
few studies left and all the riparian [1:02:03](indiscernible).
So real quick, can we go on the phone to see who's on the
phone still?
MR. SCHWAB: Yeah, this is Nate Schwab with ABR.
MS. CURTIS: Jennifer Curtis with EPA.
MR. PRICHARD: Alex Prichard from ABR.
MR. MABEE: Todd Mabee, ABR.
MR. BECKER: Hello.
MR. GILBERT: Hi. Could you introduce yourself?
MR. BECKER: Sure. My name is Earl Becker, Alaska
Department of Fish & Game.
MR. GILBERT: Okay.
MS. MCCLURE: Lauren McClure, Stillwater Sciences,
FERC consultant.
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MR. RYCHENER: Tyler Rychener, Louis Berger, FERC
consultant.
MS. FOREMAN: Alynda Foreman, FERC consultant.
MS. LONG: Becky Long, Susitna River Coalition.
MR. GILBERT: Okay. Well, that helps us a lot here. And if
people can just continue to keep identifying yourselves for our
record.
MS. MCGREGOR: Since we have Earl Becker on the phone,
can we start with large carnivores and then move on to -- is that a
problem?
MR. LAWHEAD: I don't know. Nate, what's your schedule
like? Nate's in the field and -- can we at least do bats first?
MS. MCGREGOR: Okay. We can do bats and then go to
large carnivores.
MR. LAWHEAD: Okay. So we're going to switch the order.
We'll go do bats and then large carnivores, then aquatic furbearers,
wood frogs, and the other three.
MR. GILBERT: Okay.
MR. LAWHEAD: So we're basically just moving large
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carnivores up two slots.
MR. GILBERT: Okay.
MR. LAWHEAD: I don't think that'll be a problem, because
everybody that we need is on the phone already.
Okay. So, Nate, take it away. And just let me know when you
want me to turn the slides and I'll try to anticipate.
MR. SCHWAB: All right. I'll try and say okay when I'm
ready.
MR. LAWHEAD: Okay. Speak up.
BAT DISTRIBUTION AND HABITAT USE (STUDY 10.13)
MR. SCHWAB: Good afternoon, everybody. Can you hear
me okay?
MR. LAWHEAD: Yeah. You're a little faint, but just speak --
MR. GILBERT: Get as close as you can to your microphone.
MR. LAWHEAD: Telephone.
MR. GILBERT: Telephone.
MR. SCHWAB: How's that?
MR. LAWHEAD: Better. So just clip through the first few
slides and then get to the variances.
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MR. SCHWAB: Okay. Perfect. So I'm Nate Schwab with
ABR, and I'm going to present the result of the ISR for the bats.
So the objectives for the bats was to pretty much figure out if
bats were present on site, which habitats their activity was associated
with, and to look for any potential roosting sites within the project
area.
MR. BECKER: I’m just going to get ahold of Mark Burch,
and I always say the wrong number.
MR. LAWHEAD: Earl, you're not muted.
MR. BECKER: I'm sorry.
MR. SCHWAB: So to accomplish these objectives, we use
acoustic surveys which consisted of Anabat monitoring devices,
which we deployed throughout the study area. We used 20 of these
stations that you can see on the screen, pretty widespread throughout
the project. And these stations record the echolocation activity of
bats.
We deployed these stations in mid-May and retrieved them in
mid-October of 2013.
And also to accomplish our objectives, we did two sessions of
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roost surveys. We did one roost survey session in the summer and
one in the fall. And during these sessions, we looked for artificial
roost structure sites and natural roost sites.
So two of the variances that we had for the bat study, we were
unable to sample on CIRWG lands in 2013, either acoustically or the
roost surveys. And we actually expanded the effort in 2013 above
and beyond what was in the RSP to expand our roost surveys outside
of the project area that was defined in the RSP.
So from the acoustic results, you can see all the red dots on the
map were sites where we recorded bats or detected bats, and the
yellow dots are sites where we did not. So we detected bats at 17 of
the 20 sites, all throughout the project area, and we also broke up
these -- the project area within four broad habitat types, including
stream, pond, cliff, and upland sites. You can see that the majority of
the sites and activity occurred at stream sites and pond sites.
So we also assessed the natural roosting structures for bats,
and the main source of these natural roosts were the cliff systems
above the Susitna River. So we mapped 102 cliff sections above the
river and identified them as not suitable, poor suitability, moderate
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suitability, and high suitability.
Next slide.
So in addition to the natural roost structures, we also looked
for artificial structures, which in this case were primarily cabins. We
searched 11 different sites that consisted of 26 different structures
within and just outside of the project area, and we were unable to
find any bats or evidence of roosting bats at any of these sites.
Okay.
More results from the acoustic data. So as I mentioned, we
deployed them in May and picked them up in October. And you can
see there's a pretty definitive peak activity in July and also in late
September, in the late fall there.
And these two distinct peaks in activities were part of the
decision-point process for -- which I'll get into in just a minute. But
the peak in July represents the maternity colony period, whereas the
peak in the late fall represents the pre-hibernation or migration
period. Those two peaks are important.
Okay.
So based on our findings in 2013, we recommended
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continuing acoustic monitoring, which included deploying four
detectors at the CIRWG sites, which we were unable to monitor in
2013, and to also deploy at six sites that we had already monitored in
2013.
So in addition to the continued acoustic monitoring, we also
conducted two different capturing sessions and radio telemetry
sessions for bats. One session was in the summer and the other was
in the fall. You can see the tiny radio transmitters that we used for
the bats.
So as I mentioned, part of the decision point was based on
finding these seasonal peaks in activity, both during the maternity
colony season when adults are raising pups and during their
pre-hibernation migration period. So we continued doing the
surveys.
Based on that decision point, we continued doing acoustic
monitoring, as I mentioned, at the four new sites on CIRWG lands
and at six sites that we had previously monitored in 2013.
In addition, we did the radio telemetry effort, where the July
session we had pretty poor weather, did not cooperate very much.
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We were able to capture and track one little brown myotis. We
tracked that bat to essentially three cliff sections along the Susitna
and we got roosting information for that bat over a 10-day period.
We also conducted a second period of capture and telemetry in
the fall, when obviously the weather was colder and quite a bit of
precipitation, which is not conducive to capturing bats, and we were
unable to capture any bats in the fall period.
Okay.
So we collected acoustic monitoring data in 2013 and '14 to
look at the habitats associated with bats. And we also conducted our
roost site searches at artificial structures, which were the cabins, and
natural structures which included mainly the cliffs above the Susitna.
So we did an initial evaluation in 2013.
And then can you go back one, Brian?
And then in 2014, as I mentioned, we used the telemetry to
track the bats to their specific roost sites.
Okay.
So right now we've collected all of our field data for 2013 and
2014. All that's left is to analyze the 2014 acoustic data, with no
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modifications from the ISR, and complete the data analysis of the
roosting information we collected from the telemetry effort, with no
modifications from the ISR, and then finally to synthesize all this
information for the USR.
MR. LAWHEAD: Okay. Thanks, Nate.
MR. GILBERT: Okay. That's a good presentation. So
thanks, Nate.
And that study is largely the data collection study.
MR. LAWHEAD: Yes.
MR. SCHWAB: Yes.
MR. GILBERT: So comments, anything, Phil, on bats?
MR. BRNA: It's not a migratory bird, so we're not looking at
it.
MR. GILBERT: Okay. Sarah?
MS. BULLOCK: Sarah Bullock, Bureau of Land
Management.
So you've only -- other than Anabat acoustical surveys, you've
only really tagged or radio -- or captured one little myotis and
tracked it, or did you capture any other ones to look for roost sites?
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MR. SCHWAB: No. We only captured the single bat, and
that was 24 days of effort, 24 nights of effort.
MR. LAWHEAD: So this is kind of, you know,
unprecedented research. People usually, when they do this kind of
work, they go to roost -- known roosts, and we didn't actually know.
We're kind of working backwards, detecting the bats and trying to
find the roosts, and it's pretty tricky, particularly in natural -- there's
not good records of use of natural habitats for roosts like this, in
Alaska anyway. It's true elsewhere, but yeah.
You know, the significant thing we might do is that we are
going to establish that they do roost in those cliffs, which is what we
suspected. It was a little surprising to not find them in any of the
structures we looked at.
MS. BULLOCK: Yeah. That was going to be my next
question, if you had found any in the structures, no [1:14:09]
(indiscernible), no evidence whatsoever, no feces or anything?
MR. LAWHEAD: No. Just --
MR. SCHWAB: No, nothing.
MR. LAWHEAD: Nope. And we also had some
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communication with some cabin owners, and they said they had
never seen any out there in the time that they had been using it.
Some of those were above the tree line.
MS. LONG: This is Becky Long. I wanted to ask, were there
bat studies in the '80s that helped you?
MR. LAWHEAD: No. There was one sight record of a bat
from the mammal studies in the 1980s.
MS. LONG: You guys really were starting from scratch.
MR. LAWHEAD: Pretty much.
MR. GILBERT: Any other comments for the bats?
MR. LAWHEAD: Okay. Thanks, Nate.
MR. SCHWAB: Thank you, Brian.
MR. GILBERT: Okay. We've going to switch up the order on
the agenda here a little bit and do the large carnivores.
DISTRIBUTION, ABUNDANCE, AND HABITAT USE BY
LARGE CARNIVORES (STUDY 10.8)
MR. LAWHEAD: All right. So this is a cooperative effort
between the Alaska Department of Fish & Game and ABR. And I'm
going to tag team with Alex, and I guess Earl is listening.
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MR. BURCH: Yeah. Obviously we heard Earl on the phone.
I wasn't able to get through to him, so for the sake of the meeting,
you might want to say something about what's going on here.
MR. BECKER: This is Earl. If you -- I never did get that
link. It was too long. I don't know if you can e-mail me that link and
I'll look and see what you're putting up. Right now I'm just on the
phone.
MR. LAWHEAD: Go to the web site and look under the
meetings link.
MR. BECKER: What site is that?
MR. GILBERT: Susitna-watanahydro.org.
MR. LAWHEAD: So while Earl's doing that, I'll --
MS. MCGREGOR: Earl, I'll e-mail you the link.
MR. BECKER: That would be great.
MR. BURCH: So I guess what I was going to say is the point
of this is to briefly present the ISR and then take questions, and we
anticipate questions on this, so we don't necessarily have to defend or
go into a lot of detail with descriptions. But we wanted you on the
phone so you'd be able to hear the questions and the comments, Earl.
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MR. LAWHEAD: Yeah. It's not a debate.
Okay. So the objectives are identified in the ISP and repeated
in the ISR.
Estimate population of brown bears, black bears, and wolves
using existing data, and do kind of a look at bear use of salmon
spawning habitats downstream to try and get an idea of the minimum
number of animals that might be affected if the salmon would be
affected, and look at existing data from Fish & Game on the
occurrence and use of the area by wolves.
Black bear and brown bear work consisted of two components.
One is spatial modeling of population density using existing
population survey data that the Department of Fish & Game did in
past years, and to do current snagging of hair samples in salmon
spawning sites downstream and look at DNA to identify individuals
and stable isotopes to get an idea of the diet of the bears using that
area.
And again, look at existing available data from Fish & Game
on wolves.
There were a couple of variances. The main one was the lack
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of access to CIRWG lands in the downstream area and railroad
corporation lands, plus some private lands which could potentially
have been used as hair snare sites, so the results weren't as
comprehensive as we wanted.
Those limitations should be -- have been addressed now
through the CIRWG access agreement, and we'll take a look at that in
2015 to get access to all of the sites that we wanted to look at.
And then there's a small adjustment in the area in which the
bear data were collected, the historical bear data were collected, to
focus on Unit 13E.
This describes the data site used for the spatial modeling,
density modeling that Earl worked on in conjunction with Dave -- I
can't remember his name.
MR. BECKER: Miller.
MR. LAWHEAD: Right, Dave Miller from the University of
Rhode Island, formerly of St. Andrews, and they looked at line
transect data from 1,200 -- over 1,200 transects flown in 2000, 2001,
and 2003. Developed some new methods to develop -- or to come up
with a density surface model, and then generated population
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estimates based on those data, 1,262 black bears during the early
2000s, and 841 brown bears during that same time period.
And it's also reflected in these spatially explicit maps. The
darker the shading, the higher the density. This is for black bears,
you see a tendency for lower elevations and drainages. And then this
is brown bears, much higher use of higher elevations.
And then the idea is that these data can be used in the license
application to examine the relative values of the different corridors
and reservoir inundation zone, et cetera, for the impact assessment.
Okay, Alex.
MR. PRICHARD: Okay. So this is the downstream section.
We deployed 52 single-catch cable snares that you can see in the
picture down below. The idea is that the bears walk through and it
breaks away and you get a hair sample.
Over the summer, we collected 77 different hair samples from
those 52 snares. 34 snares had samples collected. This is results
since the ISR.
We hadn't had the lab results done at the time of the ISR, but
we have since conducted -- had DNA analysis and stable isotope
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analysis conducted. We ended up with -- DNA was successfully
conducted on 37 samples from 33 different tripped snares, and we've
identified 16 black bears and 11 brown -- 11 different brown bears
using the area where we had our snares. And stable isotope analysis
was successfully conducted on 79 hair samples, and the stable
isotope analysis showed the brown bears had higher carbon 13 and
nitrogen 15 signatures than black bears, and that's indicative of
higher use of meat and salmon in their diet.
And this is just the results showing the different hair samples
and the stable isotope signature. Generally, if you go up into the
upper right, that's indicative of more salmon, and the lower left is
more plant material, so the black bears were using predominantly
plant material and there's higher variability in the brown bears.
There's moose, and other meat is in between.
So no modifications to the study plan are needed to complete
the study and meet the study plan objectives.
And for 2015, we'll continue with the second year of bear hair
sampling in the spawning salmon areas, expanding it to areas that we
weren't able to access in 2013. We'll seek additional Fish & Game
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data on wolves in the study area, and we'll synthesize historical and
current data on bear and wolf populations and habitat use. Okay.
MR. GILBERT: Okay. Good. So how about this study?
Anything else, federal agencies, questions about the carnivores?
Yes, Sterling.
MR. MILLER: Once again, I'm Sterling Miller. I'm here
representing Wild Salmon Center and Alaska -- and the Trout
Unlimited. They've hired me to look at some terrestrial species
reports.
And Kirby asked me to frame my comments in the form of
questions, and I would like to be able to do that, but I'm not able to
do that for this one.
And I'll say that it's because I believe the bear studies cannot
be salvaged to do anything and provide any information of value to
evaluating the project impact. So I'm going to make my comments to
justify that point of view and to explain why I think that.
I have been -- Earl and I are friends, or have been, and I would
like to preserve that. We've worked in the past together
collaboratively and have even published papers together.
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But I believe that this study is an example of what happens
when you have a biometrician conduct a study by himself without the
collaboration of a bear expert or a biologist to provide some
semblance of biological reality to the study.
I believe the study is flawed conceptually, and as well, even
though Earl will chuckle at this, mathematically. And so I'm telling
you what my conclusions are up front, and then I'll explain why I
have reached those conclusions.
First of all, I did -- I was a principal investigator of the bear
studies back in the 1980s. And I worked with Earl on those studies.
My wife actually hired Earl Becker. She was the chief biometrician
of those studies.
And Earl and I worked together collaboratively quite well,
with the combination of a biologist and a biometrician, on some of
those early studies. But I think since then, it's been unfortunate that a
biologist hasn't been involved apparently in the direct, you know,
implementation of these studies.
Can you put up this figure, please, Brian, this -- the large
carnivore study area from the ISR?
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I believe one of the key things is that the large carnivore study
area is an area of some 26,000 square kilometers, 26,500 square
kilometers. So those numbers that you saw, 841 brown bears and,
what was it, 1,200-something black bears pertain to this whole large
carnivore study area of some 26,000 square kilometers, right?
And you can see that the vast bulk of that study area is not in
the vicinity where any impacts from the Su Hydro studies or Su
Hydro dam impacts will occur. It goes all the way down to
the -- keeping the northern part of 16A and 16B.
And so from a managerial standpoint, trying to come up with a
population estimate or a density estimate that integrates the results all
the way from the foothills of the Alaska Range, where bears subsist
on an economy of moose calves, roots and berries and vegetation,
down to the high-density populations that occur in the Lower Susitna
area, where the bear economies are dependent on salmon -- and of
course, bear economies that are dependent on salmon support much
higher densities than bears in these interior economies, where they
eat roots, berries and moose calves. This is documented in a wildlife
monograph I wrote back in 1997, and also in the studies by Grant
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Hilderbrand who used to be regional supervisor with -- and it makes
common sense. We all know that where bears eat salmon, it supports
a lot higher density.
So what exactly the utility is of coming up with a population
estimate across that integrates all these areas from low-density bear
populations where bears occur somewhere in the density of 20 to 30
bears per thousand square kilometers, down to the lower part of that
area in 16, where, although there haven't been studies done there,
because the five species of Pacific salmon occur there, bear densities
are certainly higher than a hundred bears per thousand square
kilometers, and probably much higher than that. So you know, the
number is of no real utility to anything.
The other thing that -- point that I want to make is that -- this is
an experimental technique. And if you read closely, one of the
things that has to be done in terms of the study plans that they have
to be consistent with generally accepted scientific practices. That's in
the design.
And there has been -- there has been two papers published on
this technique, and both of them are wrong. The first paper was
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published in 2009 by Becker and Quang, and it showed the first
analysis of these data of population estimate of bears in this large
carnivore study area, which was called the Talkeetna study area in
the Becker and Quang 2009 paper, and their estimate at that time was
541 bears, brown bears. I'm talking brown bears now.
So in this current analysis, using exactly the same data, but
some additional analytical techniques, the current analysis in the ISR
comes up with an estimate of 841 bears in exactly the same area.
And the data, the new analytical techniques have not been published.
They have not been subject to peer review.
Now, for other species, they have been. You know, there are
Golden Eagle and so forth that have been non-mobile species that
have utilized similar techniques to this. But these techniques have
not been published as they're currently implemented in the -- or
supposed to be implemented, have not been exposed to peer review,
and as evident by this 46 percent increase in the population estimate
that occurred with no new data, just difference in the mathematical
techniques utilized, resulted in a 46 percent increase in the
population and density estimate. So that is one demonstration of
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how this is not a generally accepted scientific technique.
The other thing is that I've reviewed the survey and inventory
reports on brown bears and black bears which are published every
two and three years by area biologists, and none of those reports
make any utilization of this Becker and Quang technique.
Now, the one report in Unit 9 by Riley actually mentioned
some results that were conducted in Unit 9, but it just mentions the
results. It doesn't -- it doesn't utilize them in any way. And as I'll
develop later, those results are abnormally low and probably
inaccurate because of their severe underestimation bias. And you
can tell -- and what's more, those were done before the new
analytical techniques which are being proposed for this study were
implemented, so those studies that were done in Unit 9 out in the
Alaska Peninsula are utilizing the old analytical techniques, which
are purported -- reported in the Becker and Quang 2009 paper.
And if you were to reanalyze them with this new approach,
which is based on something called point independence, that estimate
would increase by a significant amount. Whether it would be
46 percent or not, I don't know. But and -- but it would increase
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significantly with point independence incorporated and their
analytical techniques.
The other thing is that the other study was done on the Togiak
National Wildlife Refuge in Unit 18, and that study was done by
federal biologists and was adequately reported in a European journal.
And I have been in touch with the people who did that study.
It was using the original analytical techniques that were reported in
the Becker and Quang 2009 paper. It's not even mentioned as an
application of a technique in this report. But it -- I've talked to the
people involved in that study, and they agree that that's an
underestimate and a serious underestimate because of this new
analytical technique involving point independence.
So you know, we can contrast this -- these results a little bit.
Earl and his colleagues estimate 841 bears in this 26,000 square
kilometer area. If you want to compare that with the results that I
produced for a study in the 1980s which was focused on estimating
the abundance of bear in the actual vicinity of the proposed Watana
impoundment, I -- I came up with, let's see -- let me see -- 35 bears.
And so the difference between 35 bears -- brown bears in the
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area of the proposed impoundment and 841 bears in this huge area,
just it illustrates the fact that this study area is completely
inappropriate for estimating the abundance of bears with relation to
the hydro project.
And the same thing is true of the black bears. I
estimated -- the slides show that there was an estimate of some 1,200
black bears in this huge large carnivore study area. I think my earlier
studies in the vicinity of the Watana impoundment came up with an
estimate of 47 bears.
So somehow there's a disconnect here, and what is being
proposed in the final -- or in the initial study report is that somehow
they are going to take -- the original studies were done by randomly
selecting 35-kilometer long transects below 5,000 feet elevation and
flying those transects using something called a double-blind
technique, where the observations of the pilot and the biologist are
assumed to be independent.
And the -- those techniques are highly sensitive as a study by a
woman named Benson from the University of Alaska Fairbanks
showed. Those studies are highly dependent on the assumption that
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the observations between the pilot and the observer are independent.
She did some simulation studies, and if there was any degree of lack
of independence between the pilot and observer, that means if the
fact that one of them sees it makes it more likely that the other one
will see it, that will result in an underestimate of bear abundance.
There is no way that it can go the other way. There is no way that
you can generate an overestimation bias by lack of independence.
It's always an underestimate bias.
The -- I was going to say both the black bear and brown bear
population estimates are in an area way too large to be of
management since, plus, you know, there is very likely an
underestimate bias. Part of the reason I think there is an
underestimation bias is because when, even after using the 841 bears
that they came up with more recently, even after you do that and
integrate across the whole area, you have, you know, somewhere in
the northern or the -- you know, the northern and eastern part of the
study area where bears are living on interior bear economy, in those
areas density is somewhere between 20 and 30, and the other half of
the study area, where the bears are depending on a salmon economy,
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there's somewhere in excess of 100 bears per thousand square
kilometers. So if you integrate those two things, you've got to come
up with a much higher density figure than was presented in this
report.
And in fact, this report doesn't even provide the density
estimation figure. I had to calculate it myself.
So the way that the Becker -- the ISR proposes to make a
division and extrapolate from their data, which were collected in
2000 and 2002, as it said, to the study area, is they're going to
subdivide these 35-kilometer-long transects into 1-kilometer
transects and describe the geographic characteristics -- I mean, the
physical characteristics of each of these 1-kilometer-long segments
of the 35-kilometer and then use that to extrapolate to get an estimate
of abundance for a much smaller area.
And this is where I think the real serious problem occurs with
this technique -- I'll make it one of many serious problems -- is that
the underlying assumption here is that the components of habitat or
the physical aspects of habitat that you see looking out the window
of an airplane are pertinent to bear abundance and bear density. And
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in fact, they're not.
And if a bear biologist had been involved in this study, you
could have determined it would have been -- I'll give you an
example. You can look at a salmon stream out in the Alaska
Peninsula as winding through some tundra with some dwarf willow
and alder along it, and you can look at a salmon stream up in the
center of Unit 13 or north in the Alaska Range that doesn't have
salmon on it, but they look exactly the same. But the -- it’s wrong to
say that just because they look the same, they have the same density.
They don't. Because the density of bears is dependent on what
they're eating and how much of that -- and how it's distributed.
And you can't tell what they're eating looking out the window
of an airplane. Plus the fact that bears spend a lot of time commuting
between different patches of places where there is food, and so the
fact that you see a bear in some particular place, looking out the
window of your airplane, doesn't mean that the characteristics of that
place where you see that bear or that bear group is pertinent at all to
extrapolating to come up with a number of bears in areas of similar
habitat. It just doesn't -- it's just wrong. It doesn't work that way for
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bears.
I have some comments on the DNA -- or on the nitrogen
isotope studies, but basically I'm not going to make those comments
because I think those are minor compared to what I'm saying now.
And I think it's good to get some feedback on what I said.
The -- the estimates of density that have come up are also
completely -- using this technique, are completely -- are low with
respect to other estimates of density that have been attained using
other techniques for areas of similar habitat. They're just -- they're
just low.
The first estimate that was -- that was derived in this large
carnivore study area of 541 bears based in the Becker and Quang
2009, the confidence intervals around that estimate don't even
incorporate the current estimate of 841 bears.
So it just goes to show, you can do all kinds of math and fancy
math. It makes no sense whatsoever. And the proof of that is the
fact that you had a 46 percent increase between the original estimate
of the number of brown bears in this area and the current estimate.
So with that, I'm sure I've given Earl plenty to talk about and
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respond to, but that's the -- I have more comments in addition.
And I hope that our friendship, Earl, will survive this.
MR. LAWHEAD: Before --
MR. BECKER: (Indiscernible - interference with
speaker-phone.) [1:41:18]
MR. LAWHEAD: Wait, Earl -- whoa, Earl -- Earl, wait a
second.
MR. BECKER: [1:41:20] (Indiscernible - interference with
speaker-phone) I don't agree with much of what he said.
MR. LAWHEAD: Earl, wait a minute. Can I make a remark,
please?
MR. BECKER: Sure.
MR. LAWHEAD: This is where -- I know this hurts, but we
don't want to get into a big debate here. If you can kind of focus
your response on some of the main points that Sterling brought up.
And the ones I heard were potential differences of study areas,
differences in density throughout different parts of the study area we
identified, and then also the habitat classification, which to my way
of understanding was more about evaluating sightability than it was
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about evaluating actual habitat use by bears.
So take it away, Earl.
MR. BECKER: I think the disconnect, Sterling, is you don't
understand the math.
So anyway, basically the purpose -- the original study was
done to estimate bears -- basically we wanted 13E. The Park Service
wanted part of it, so the study area was made bigger to deal with their
part, and we could generate sub-estimates from that. So that's what
the original data was collected for.
Now, the Becker–Quang paper, there is a population estimate,
and then what we -- what we found out was the -- there is an
assumption that under Becker–Quang that you have independence of
observations between the pilot and the back-seat observer. In a
Super Cub, they sit directly behind one another.
And they found out -- there is a very important paper, I sent
that to you, Sterling -- Borchers 2006, and [1:43:07] (Indiscernible)
has done a lot of work since then. And they said, well, gee, you
know, these double -- double survey -- mark -recapture distance-
sampling surveys, where we assume total independence, there is
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some real problems with that. It's generally not true. It's not true on
whaling boats, it's not true on small planes.
So these big -- these big ocean-going ships that they use for
whale -- to get whale estimates, they have the same problem. They
all suffer from the same problem. If an animal -- whale, bear,
whatever -- is easy to see from one observer and they're both looking
at the same time, that animal is most likely easy to see by the second
observer. It's not a random shuffle. There is a dependence there.
So that's why you talk about the estimates of change. Yeah,
we recognized there was a problem and so we immediately stopped
analyzing data that way and went and worked on a fix for it. And so
we came up with a new method.
Well, the method -- the point independence, basically what
that says is -- here's what you're doing with the data. You have
distance sampling data with covariates that model probability of
detecting the animal, assuming that there's some distance out there
where the animal's perfectly detected.
Sterling and I would both agree that that's not a very realistic
assumption for brown bears, or black bears for that matter. And so
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we collected double-count data, pilot/observer independent, and it
was collected as independently as can be, to try to then estimate how
many we were missing, to make an adjustment. And so that's called
mark-recapture distance sampling. You have a mark-recapture
component, you have a distance-sampling component, and you
basically have two models you're putting together. And so most
mark-recapture estimates assume independence between the two
observers. They always do. And that's what we used.
And Sterling's right, that can be a problem. And Borchers's
2006 paper pointed that out.
And so we -- we went to correct for that, and it took a while,
because we actually had to create a new detection function in order
to solve that problem, in order to get one that was consistent with a
mark-recapture point independence assumption.
And what that says is there's one distance where detections are
the highest is where you're going to make the adjustment. So think
of it this way. We used distance-sampling modeling with covariates
to get the general shape of the detection curve, and the mark-
recapture data, assuming that that peaks at 100 percent or a
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probability of 1, just moves the whole curve down to the appropriate
level.
And it's not quite as simple as that, because when we use a
mark-recapture model, that thing shifts up and down for each
observation. For instance, the percent cover is in my mark-recapture
model, and let's say my apex is a hundred meters, that -- so how
much that detection curve shifts up and down is a function of was
that bear seen in zero percent cover or 40 percent cover? And so the
whole thing will shift up and down.
And so the point independence, it's been pointed out, we've
seen the same issues with seal surveys, marine mammal surveys, that
NMFS has spent millions of dollars on.
And in 2006 there is a mathematical solution to that. It's all
been peer-reviewed. It's in lots of papers published. I'm currently
reviewing a paper on bear estimation using the same technique, and
there's two papers by Stapleton that have already been published on
polar bears. So using the same -- same general technique.
They use a different detection function than we do, which may
or may not be problematic. So -- but -- so the methodology, in terms
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of generating a population estimate, you can -- it works fine.
It's been peer-reviewed. I have a paper on this that's under
review right now. So that's the -- the spatial modeling. There's been
lots of papers on that. That's been peer-reviewed. So you know, it's
all peer-reviewed.
So there definitely was a dependence issue that raised the
previous population estimates, and that was -- that was the
independence of observer issue. Basically if you're looking -- you
know, you're in the same aircraft and if the pilot sees an easy-to-see
bear, is that a coin flip where it can be hard or easy to see, or is it
most likely an easy-to-see bear for the back-seat observer?
Well, most likely. Not always, but most likely it's going to be
an easy-to-see bear for the back-seat observer. Well, that's a
dependence issue.
And so point independence says, well, basically the only error
is that -- how can I put this another way? And so you're just -- the
amount of adjustment you're making at the very apex is not very
much. Basically what happens, if you try to take a mark–recapture
model and modify the probabilities and use the mark –recapture
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model over all the differences, rather than just the peak of the
detection curve, you get distortions due to dependency issues. And
that's what caused the underestimate.
So it's all peer-reviewed, and the population estimates are
about as good as you can get. And so that's not a problem. It's peer-
reviewed. You know, Sterling doesn't understand the math. I'm
sorry. It's very complicated mathematics, I will grant you.
So really the only other issue I heard was about, well, you
know, the study area is so big and you need to focus it right here
where the dam was.
Well, the reality was, that's one way to go about -- and that's
the more traditional way to go about generating an estimate of what's
going on. But the -- the impact of this project for terrestrial wildlife
is not just the dam. There -- there are questions about which -- which
of these road access -- you know, at the time we did the analysis,
which you know, eastern road access and northern road access,
maybe some other road access, so these are going to have the bigger
impact on the terrestrial wildlife, and any other footprints that they
come up with, secondary development issues or whatever, how are
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you going to make inferences about that?
So one of the things that the people at St. Andrews were
working on when I was at St. Andrews solving this particular
problem -- the State of Alaska sent me to St. Andrews, which is the
place where all the top distance-sampling people in the world work at
-- I was there for the summer -- is that they were -- they were doing a
lot of spatial modeling.
And I looked at that and said, you know, that has real
implications for us in some applications. So you know, for Fish &
Game, an estimate on the number of black bears and the number of
brown bears in 13E, look at a harvest rate, that might be sufficient
statistics in terms of regulating harvest. May or may not, but it very
well could be. So certainly it's a first cut.
Then we have other issues, like we put this project right here
or this or that, where it's not a sufficient statistic. Just generating an
average black bear density or average brown bear density applied to
the footprint of the roads and impoundment dam would not be right.
I agree with Sterling on that. And so --
MR. MILLER: I said the opposite.
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MR. BECKER: So what we do is we did spatial modeling.
And the spatial modeling looks at covariates so it can be generated
from a GIS level. It has nothing to do with what I see out of an
airplane. The GIS segments of where the transect segment was and
where the bear observations were then are correlated to the GIS
layer, what we pull out of that -- that band we're looking out -- let's
see here, 450 meters for black bears, so 22 meters to 450 meters, and
we're on that one segment transect band. We characterize the slope,
aspect, vegetation cover, and for some GIS layer, and I can't
remember -- LANDFIRE was the one that we used, the most
common one available. It may not be the best, but it was the one that
we used.
And so now, what this -- this GIS layer does, it has an
XY -- there's an XY coordinate system variable in the spatial model,
and so what that does -- so there's a north, south, east, west gradient.
So for instance, in black bears, the northeast corner of that
study area is total black bear habitat in the spring. And so by putting
this east–north -- there's an east–west -- so by putting this gradient in
there, if you have densities changing basically as you go east to west
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and north to south, that variable adjusts for that, and then what it
picks up is whatever -- whatever comes out of the spatial modeling.
And for black bears, it was -- it made perfect biological sense.
It was an interaction between southern aspect and slope and lower
elevations. These are the first areas that green up. They're -- and so
that made perfect sense for modeling spring distributions of black
bears.
But the spatial model for brown bears didn't -- it wasn't
particularly great. It wasn't bad, but it wasn't -- it wasn't near as nice
as it was for black bears, because black bears are more keyed in on
these certain aspects and brown bears are -- and at this time of year,
probably running around looking for carrion. So in some of them,
some of them are just trying to stay away from bigger bears with the
young, but they're -- nevertheless, it made sense to use a spatial
model.
And what we didn't do because the -- they hadn't come up with
a -- you know, where the access was. The only thing that seems to
be fairly well nailed down is where the dam is, where the access
roads were and stuff, what the footprint was going to be, so we -- we
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can certainly generate an estimate of the impact of this project based
on these density values, because we estimate for every square
kilometer. We estimate the number of bears in each square kilometer
out there, and that's a huge study area. So we can generate way more
realistic estimates of the number of spring bears, whether it be black
or brown, impacted by this project once the exact footprint of the
project gets fixed, and then there's some agreement on how big
should the buffer zone be, should it just be the level of the
impoundment, should it be 500 meters, three miles, ten miles from
the impoundment, from the road, all that type of thing. And that's
where I would want to talk to a bear biologist.
But the mathematics of getting it all set up are the mathematics
of getting it all set up. So the bear biologist that doesn't understand
heavy math isn't going to be of much use.
So I don't know. Is there -- Brian, are there other subjects you
wanted me to address?
MR. LAWHEAD: No. I think we've about killed them.
MR. MILLER: I was going to ask one question. In that lower
part of that distribution there, is Earl contending then that the bottom
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part of where it's all gray there, in the south -- southern part of that,
has a lower density of bears than that blue partway up in the upper
right? Is that your contention, Earl?
MR. BECKER: Hold on. My screen went blank. I've got to
turn it back on so I can look at the map.
MR. MILLER: I estimated a bear abundance in that upper
right portion, and it was lower than in the Su hydro project, not
higher. And certainly there are no salmon up there. And so there's
bound to be a lower density in the upper right --
MR. BECKER: Hold on here, Sterling.
MR. MILLER: -- than in the lower --
MR. BECKER: Hold on. Stop. Let me answer the question,
all right? Just stop.
So your question is in the spring, so repeat -- now I have the
math in front of me. Just repeat your question. Not your
commentary, just your question.
MR. LAWHEAD: Before you do, let me make an
observation. These surveys are conducted in May, after bears have
emerged from hibernation and before leaves have emerged on the
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vegetation, which is the only time you can really see them. So it
does reflect --
MR. BECKER: It's the same time Sterling does his mark–
recaptures. It's the only time aerial work --
MR. LAWHEAD: Right. It's just context for --
MS. MCGREGOR: And it's before salmon are present.
MR. LAWHEAD: -- for the other listeners.
MR. MILLER: But there are no salmon in the upper right
there, in the headwaters of the Susitna River.
MR. GILBERT: He just wants you to restate the question.
MR. BECKER: I understand that. And so you're just saying
there are some hot spots up there?
MR. MILLER: There's some blue spots.
MR. BECKER: And so how did that come to be?
MR. MILLER: Yeah.
MR. BECKER: Is that your contention?
MR. MILLER: Yeah.
MS. MCGREGOR: What's blue?
UNIDENTIFIED MALE: He wants to know what the blue
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spots represent.
MR. BECKER: Oh, okay. Well, the gray spots are areas in
the spring that are considered too high to be brown bear/black bear
habitat, based on the data we collected. We surveyed elevations way
higher than this, and based on when we weren't seeing any more
black bears, we had one at like 4,600 feet maybe -- I might be getting
my study areas confused. But you know, it varied by species, as the
brown bears go higher than black bears. But it varied by species as
to how high was too high to be non-habitat for that species, for that
spring period that we did the survey in.
It doesn't mean if the snow melts and you get vegetation up
there, they won't go up there higher in the year. But for the time
we're making inferences about, which was this ten-day/two-week
window that Brian is talking about, as mentioned, that's what we're
making inferences about.
MR. LAWHEAD: So you called it gray. To us on the screen
here, it looks bluish. But basically it's elevation -- it's out of range
due to elevation.
MR. BECKER: It's out of range because it's too high to be
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habitat.
MR. MILLER: This is the area where probably the highest
density of brown bears occur.
MR. LAWHEAD: He's looking --
MR. MILLER: Salmon, salmon there, in the whole area.
MS. MCGREGOR: Not in --
MR. BECKER: Well, Sterling, you might think that, but that's
not what our -- we collected data. You've never worked there, so you
just have an opinion, but we've collected data. That's not where we
saw the bears.
MR. MILLER: Well, see, that's the problem. The difference
between us is you conflate detectability with bear abundance. And
down in this area, it's all forested, so you can't see bears down in that
area. And so that's why --
MR. BECKER: You use a multiple covariate to adjust for
that. That's adjusted for. Yes, they're harder to see bears. That's
adjusted for. You don't understand the mathematics. That's adjusted
for.
You know, I would agree, if humans weren't involved, that
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you would have higher densities, but you know, we see those kind of
higher densities down on the end of the Alaska Peninsula where there
aren't humans. I doubt very much we have that kind of high density
on the Kenai, despite the fact that the salmon would easily support
that for bears, because of all the human inroads in the bear habitat,
DLPs, and the like.
And so -- now, one thing that we did do in these particular
models is we did use distance to salmon river and salmon spawning
stream as described by the Fish & Game -- Alaska Department of
Fish & Game -- sport fish anadromous waters catalog, and that was
not an important covariate. I thought it would be. I went through a
lot of effort to have people digitize that in because I thought for sure
that would be an important covariate, but it was not.
And I understand that there are certain locations that Sterling's
work has pointed out, like Prairie Creek that are very important for
interior bears, because basically the fact that you have salmon along
some of these big rivers doesn't mean a bear can get the salmon. It's
usually at the spawning grounds and other locations like that that
they can get the salmon. And Prairie Creek did show up as a
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spawning ground.
MR. LAWHEAD: Okay. Thanks, Earl.
MR. BECKER: Uh-huh.
MR. GILBERT: We're going to kind of keep moving on.
MR. LAWHEAD: Yeah. We're -- I understand it's clearly a
complex issue. There are -- there are strong feelings on both sides of
it. This is giving us a good idea of what Sterling's concerns are and a
preview of what his comments will be, and now you have an
opportunity, Earl, to begin to prepare.
MR. MILLER: I'd like to make just one more point and it's
unrelated to things that have been said beforehand.
But one of the things about the complexity of this report that
Earl said is exactly right. I spent -- more than half the time I spent
preparing comments on these terrestrial mammal reports I spent on
the bear report, because it was almost impossible to understand. I
had to consult with four different biometricians to be sure that my
comments, you know, made sense to them, because I was uncertain
about the math because the math is incredibly complex.
But you can use complex math to cover up a whole range of
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biological errors, and I think that's what's going on here. And if
you -- my point is, is that for the final report it needs to be in a form
and in a language that's intelligible to the people who are trying to
make sense out of it. And I bet you that there's nobody in this room,
including me, that fully understood what this report was about.
MR. GILBERT: Yeah. We need to stick to kind of just the
facts of the matter, not so much -- as much as possible, and if they're
hard to interpret, which they probably are, that does pose a challenge.
But we have to go with the facts of the study and the peer review.
But we need to keep moving, because we have five more to do
and we don't want to shorten the riparian -- I mean, the botanical
studies this afternoon.
MR. LAWHEAD: But before we go on, are there other
comments?
MS. MCGREGOR: Are there other comments?
MR. GILBERT: Any other comments by other people? And
we also covered wolf in this study, too, right?
MS. MCGREGOR: Well, and I think Sterling had other
comments to other aspects of this study, didn't you?
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MR. MILLER: Well, I think in the interest of time, I covered
my most important ones. But I do have comments on the wolf
studies.
MS. MCGREGOR: Okay.
MR. GILBERT: Okay. Yeah. And it's not that -- it's hard to
gear it right, but we do want to hear what your idea is on
modifications. I mean, that's part of the purpose here, is you have a
proposed modification list.
MR. MILLER: Well, my proposed modification is that you
conduct studies that will estimate bear abundance in the area where
it's pertinent to the dam impact.
MR. GILBERT: We've got that part I think, yeah.
MR. MILLER: The up --
MR. LAWHEAD: Could you indicate what you consider that
to be?
MR. MILLER: Well, I did that in my studies in the 1980s. It
was a 1300-square kilometer area that we estimated bear population
in right around the Watana Dam curve. That's where we came up
with our estimate of the number of bears that would be impacted by
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the project.
I mentioned what that was, and I think it was 35 -- 35.7 brown
bears, as opposed to 841 in this current study. So to estimate the
bear abundance in the area that it's pertinent to the actual impacts,
that's one study.
MR. BECKER: I guess you didn't hear me, Sterling, because I
said we could estimate any subarea we want. And so if somebody
gave me that boundary, we would generate a population estimate and
variance for that --
MR. MILLER: And what I'm saying --
MR. BECKER: -- in a much more detailed model that
accounted for things like changes in vegetation where we saw the
bear, to account for differences in capture probability, which the
general mark–recapture estimate does not.
MR. MILLER: And what my point is, that I think that that
estimate would be wrong.
MR. BECKER: Well, that's fine, but that's just your opinion
because you don't understand the math.
MR. LAWHEAD: Okay. We're getting his -- we're getting
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his comments, his concerns, and clarification here.
Anything else?
MS. MCGREGOR: Any comments for the wolves?
MR. GILBERT: Yeah. Why don't we just go to wolves.
MR. MILLER: Do you want me to just, without any
production, just --
MR. LAWHEAD: Well, if you have --
MR. GILBERT: Well, anything that you have based on this --
MR. BECKER: Excuse me. Are we done with bears?
MS. MCGREGOR: Yes. Thanks, Earl.
MR. GILBERT: For now, unless there's other comments,
Earl.
MR. MILLER: Thanks, Earl.
MR. BECKER: If we're done with bears, I want to go. I've
got other stuff to do. So let's do all the bear stuff so I can go, please.
MR. MILLER: I will make one other comment, because Earl
and I have a long history of friendship and collaboration.
I offered Earl the opportunity to review my draft comments a
couple of months ago, and he declined that because he was too busy
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at other things. But that was -- that opportunity --
MR. LAWHEAD: That opportunity is coming up.
MR. GILBERT: As Wayne says, we want to be tough on the
issues, easy on the people. That's been our moniker going all the
way back.
MR. MILLER: Fair enough.
MR. GILBERT: So just let that help you.
MR. MILLER: Do you want me to go talk about wolves?
MR. GILBERT: Please, yes. Please.
MR. MILLER: The -- on both --
MR. BECKER: Okay. Goodbye.
MR. MILLER: I have one more comment about bears, just
generally, and that is that none of the -- at best, if everything works
perfectly in this study, would have -- do nothing but generate a
population estimate. All of the other components, in terms of impact
assessment and the use of the bears by the impoundment area, would
not be addressed. All those habitat components would not -- at the
very best, all that can be done is estimate a population estimate.
That's all they're really doing, even if it worked. My proposal is that
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it doesn't work.
But to try to estimate habitat use, you need to put out some
radio collars like we did in the '80s. And with GPS collars, you
could do that and it would be a terrific advance on the studies that we
were able to conduct in the 1980s because of the -- as I mentioned
for the moose and the caribou, the higher resolution you could get on
habitat use by using GPS collars.
So that's my other recommendation, in terms of what you can
do is to define your study area better and use some technology that
will allow you to evaluate habitat use.
MR. BECKER: And I'd just point out that (indiscernible) data
is often used that way, and they don't use radio collars.
MR. MILLER: There are other ways of doing it, you're right.
MR. BECKER: There are other ways of doing it. And this
would -- this would be similar. We have lots of bear observations
tied to different physical characteristics. And so whether you see it
with your eyeball or whether you get a point from a GPS radio collar,
it's the same data.
Granted, you could sample at night and other kinds of periods
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that you're less likely to sample from an aircraft. But other than that,
once you sort of have the data and the data set, the analysis is sort of
the same.
MR. MILLER: The occupancy data would --
MR. BECKER: The mathematics is exactly the same.
MR. MILLER: Occupancy data works very poorly when you
have very small numbers of observations. You need lots of
observations in order to…..
And that's why it works with the wolverine, because you have
lots of observations because you're following the track of the
animals. But with bear, you see it once and that's your one
observation.
So try to determine occupancy models based on the very small
number of observations, it had very low power.
MR. BECKER: 365 data points, Sterling, that's not a small
data set.
MR. MILLER: And how many of those were in the upland
areas in the Watana Dam area?
MR. BECKER: Well, I mean, you know, that -- you know,
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you'll only be more precise if you went and radio-collared them, but I
don't think you're going to get that much of a different story, to tell
you the truth.
But we propose this because, quite frankly, there is a way to
get in the spatial modeling for Fish & Game, get that worked out, and
have the power authority pay for it and they provided good estimates
for the decision-making process. There is no interest in Region 4 to
do any radio-collar work. There wasn't any interest by anybody to do
the type of work you talked about. Everybody had other jobs and
more important priorities. So I offered this up.
MR. LAWHEAD: Okay.
MR. GILBERT: Okay. Let's move on. I think the points are
made. I think we captured it.
MS. MCGREGOR: Okay. So can we kind of have comments
about wolves?
MR. GILBERT: Yeah, wolves.
MR. MILLER: All right. One of the things that I think is
happening here is that the Alaska Fish & Game Department has lost
interest and concern over what happens to large carnivores over
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much of the state.
Unit 13, where this occurs, is an intensive-management area
for wolves where the objective is to reduce wolves dramatically to
increase moose and caribou populations.
Also it's implicitly a bear reduction program. The
management objectives for Unit 13 are to reduce the bear population
by 70 percent. Now, it's not designated as a bear population or bear
intensive-management area, but if you look at the management
objectives, it clearly is.
I did a paper a couple of years ago in which I documented the
trends and bear harvest regulations around the state under intensive
management. I have a copy of that paper here. But it's clear that
over much of the state, the bear -- the Fish & Game is trying to
reduce both wolf and bear populations. Not everywhere, not on
Kodiak, not on the Alaska Peninsula, but most other places.
So that, I think, shows the disinterest really in trying to figure
out what's happening in wolf and bear populations. The reason Earl
mentioned that nobody stepped up to say that, yeah, we can do better
studies than this on bears in Unit 13, because nobody really cares if a
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project impacts. But I think FERC should care.
MS. MCGREGOR: I think we need to separate Fish &
Game's management objectives from the purpose of these studies.
MR. MILLER: Right.
MS. MCGREGOR: These studies are to collect baseline data
specifically for this impact assessment. And we did go through
almost a year-long process for study planning. So it's not just tied to
what Fish & Game is doing in their management objectives for
certain areas. So I just want to --
MR. MILLER: Right. My point is, why did nobody submit a
study plan that was comprehensive along the lines of caribou and
moose? And they're even doing more for wolverine than they're
doing for bears and wolves. What they're doing for bears and wolves
are technique development in this technique that Earl talked about,
and also on wolves they're just doing -- continuing to do their routine
monitoring. They're not doing anything special for wolves, as I've
been able to determine, for the wolf studies. They're just continually
doing the routine monitoring of wolves.
And so one of the comments I have on wolves is that the scale
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at which projects are being conducted is not mentioned. So I don't
know what scale these population estimates will be derived at. Will
they -- will they become number of wolves in Unit 13, Unit 13E
where the impoundment is or the impoundment impact area? We
just don't know.
They said there's an objective of estimating wolf abundance,
but there's no indication of what geographic area those estimates will
pertain to.
And clearly my comments about the huge size of this large
carnivore study area, which is -- you know, there's not even any
indication that they're planning on estimating wolves in most of that,
because it's not even in Unit 13. A lot of it is in Unit 16, and they
can't estimate wolf abundance in 16 because of the trees. That's the
same why it's difficult to estimate bear abundance, because you can't
see them because it's forested. So the scale is an issue that needs to
be impacted for wolves.
The earlier studies done by Ballard on wolves
estimated -- identified nine wolf packs in the immediate area of the
impoundment area. There is no indication. And of those nine wolf
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packs, he estimated the number of wolves would vary from year to
year in each of those, and there's no indication that any kind of data
like those are going to be collected. So we won't know the impact of
the dam on wolf packs.
Now, part of the reason for that is because when you put out
radio collars on wolves in Unit 13, they're killed almost immediately
by wolf hunters. And in fact, Howard Golden was doing the study
trying to estimate wolf population identity in Unit 13A and B, and he
had to cancel that study because almost immediately all his collared
wolves were shot and the collars showed up on his desk.
So given inherent management, it's understandable why you
can't do a radio-collar study on wolves, because those collars have no
persistence. But if you're trying -- one of the objectives for wolves,
objective 3 is to describe the seasonal distribution of and habitat use
by wolves in the study area using existing data from ADF&G.
Now, what is the existing data? I have no idea what existing
data means to determine habitat use. The closest I can think of to
existing data are the studies by Ballard back in the '80s, and those are
clearly no longer pertinent because of the intensive management that
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has been going on for wolves in Unit 13 for many years.
So I just don't know how this objective 3 on seasonal
distribution and habitat use is going to be accomplished. The largest
pack that Ballard studied at the time was something he called the
Watana pack, and that's exactly what -- in the area that would be
most impacted by the proposed project.
So I think that -- I think that the -- the wolf studies are
basically just a continuation of routine collection of data that Fish &
Game needs for its management objectives, but has nothing to do
really, as near as I can determine, with trying to provide information
that's pertinent to this licensing application.
Thank you. I appreciate your patience.
MR. GILBERT: How about anybody else? Any other
comments on large carnivores on the phone or otherwise?
MR. LAWHEAD: Okay.
MR. GILBERT: Well, let's keep going then.
MR. LAWHEAD: Thanks. Next is Aquatic Furbearers, Study
10.11, and Alex Prichard is going to take care of this one.
Alex, are you there?
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MR. PRICHARD: Yes, I'm here.
MR. LAWHEAD: Okay. Go ahead.
AQUATIC FURBEARER ABUNDANCE AND HABITAT USE
(STUDY 10.11)
MR. PRICHARD: Okay. I'll go through this quick.
So it's study of aquatic furbearers: river otters, beaver, mink,
and muskrats.
The objectives were to delineate the distribution of beavers
and get an estimate of population size; describe relative abundance of
river otters, mink, and muskrats; look at some of the habitat
associations of aquatic furbearers; and review available information
on food habits and diet of piscivorous furbearers, and collect hair
samples from river otters and mink for baseline tissue levels of
mercury.
So different components, we do beaver and muskrat
surveys -- aerial surveys of beaver colonies in the fall and spring,
aerial surveys of muskrat pushups in the spring, track surveys for
river otter and mink during the winter, and then literature review of
food habits of river otter and mink, and hair samples.
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Okay. Study variances, we increased the size of the beaver
survey area slightly, to include the riparian mapping area along the
Susitna River.
And then the -- our planned survey of muskrat pushups for
2013 wasn't conducted because of the late spring and logistical
difficulties, so instead of doing a dedicated survey, we had
researchers who were out there for waterbird studies and eagle and
raptor studies record muskrat pushups that they saw.
And then we weren't able to get any river otter or mink track
surveys done that first winter, again, due to logistical problems and
trying to hit a weather window for track surveys, which is difficult
with -- we were restricted to certain snow conditions in that survey,
although we did -- did collect incidental observations of river otters,
river otter tracks, and other aquatic furbearer information from all the
other surveys that were going on out there.
So the results: we conducted an early October beaver survey in
2013, located 186 beaver colonies, beaver lodges, and 37 percent of
those were determined to be active based on a cache of -- a food
cache.
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We compiled 60 incidental observations of river otters and
river otter tracks, and 14 observations of muskrats and muskrat
pushups by other studies. And we reviewed the scientific literature.
Okay.
So this is the surveyed area for the beavers in 2013: the --
called the corridors, the inundation zone, and the Susitna River from
the dam site down to Talkeetna, the associated riparian area.
The red dots, which are hard to see, are active colonies, and
the yellow dots are inactive lodges.
Go on to the next one.
And these are incidental observations of river otters, muskrats,
and mink. You can see we had pretty good sample of incidental
observations widely spread out throughout the project area, as
expected, clustered around streams for river otters.
Okay. Next one.
So we -- since the ISR, we did conduct two track surveys for
river otter and mink last spring, in March and April.
We conducted a survey in May to assess overwinter survival
of the 53 active beaver lodges that were located the fall before. At
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least 39 percent of them were determined to be -- to survive the
winter. That's kind of a hard survey to do, and I think probably the
actual percentage is higher than that.
And we deployed eight hair snares for river otters in two
locations last spring to try to get hair samples from river otters, but
we were only able to get a single sample of four hairs for river otters.
Okay.
Okay. So proposed modifications, a change in the corridors is
one. And then we -- as I said before, we expanded the beaver survey
area slightly and then the objectives and methods related to the
mercury analysis were consolidated under Study 5.7, that other
people have talked about.
And the Chulitna Corridor has been dropped from the study
area.
Okay. So steps to complete the study, we conducted a second
aerial survey just this -- this fall, in September and October. And
then we'll go back up in the spring and see how many of the active
colonies survived this winter.
We'll do additional aerial surveys for river otter and mink
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tracks this winter, of course, pending the occurrence of suitable
snow. An aerial survey of muskrat pushups will be done next spring,
and then we'll do data analysis for the USR.
MR. LAWHEAD: This is pretty much just repeating the same
thing here.
MR. PRICHARD: Okay. Yeah.
MR. LAWHEAD: Okay. Thanks, Alex.
MR. GILBERT: So do we have interested parties on this one?
Any proposed comments and modifications, thoughts?
MR. LAWHEAD: I should mention that that hair-snag
attempt for otter hair didn't actually produce those hair samples in a
direct way. The guy who was checking the snares found a spot
where the otter had rolled in the snow near the snag, and he picked
up the hair, so that's what the basis was for the analysis.
The other -- the other thing that -- it's been discussed under the
mercury study, but the original intention was to try and obtain pelts
from trapper-harvested animals, and none were turned in for sealing
in that area for the first year.
And then last winter, they managed to get one otter and two
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mink from farther down, downstream, near Chulitna. And so those
were analyzed in addition to those four hairs that we got. We
actually did get mercury content on the four hairs, 0.27 milligrams
worth of hair.
All right. Moving on, we'll go to wood frogs, and that's Todd
Mabee. Hold on a second here. Todd, are you still there?
MR. MABEE: I am. Can you hear me okay?
MR. LAWHEAD: Yeah.
MR. GILBERT: Sure.
MR. LAWHEAD: That’s great. Okay. Take it away, Todd.
WOOD FROG OCCUPANCY AND HABITAT USE
(STUDY 10.18)
MR. MABEE: Okay. Yeah. We'll talk a little bit about wood
frogs today.
And the objectives are to review the existing data on habitat
use and distribution, estimate the occupancy rate for breeding wood
frogs, that was one of the main focus of the studies, use all this
information on habitat occupancy and habitat use to estimate the
habitat loss and alteration expected to occur from the development of
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the project. That will occur later.
And then lastly, to sample frogs opportunistically for the
presence of the amphibian chytrid fungus.
Study components consisted of the auditory field surveys,
where we would conduct a five-minute survey at water bodies and
wetlands, the occupancy modeling and habitat associations, acoustic
monitoring, which was done using detectors to record frog calls
throughout the time of day, and then the chytrid fungus bioassay.
The Study 10.18 variances -- variances were minor and
centered around how we selected our sampling locations. They were
adjusted for a few different reasons, the first being that the habitat
mapping and fish presence data were not available at that point in
time.
Second being that access to the sites on the CIRWG lands was
not permitted, so we were unable to survey the Gold Creek Corridor.
And then lastly, the diurnal timing of field surveys was
adjusted slightly because of logistic challenges.
Okay. So for 2013 results, starting with auditory surveys, we
sampled 90 wetlands and water bodies that were selected at random
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between May 30 and June 8. And frogs were widely distributed from
lower elevation to high-elevation habitats, from forested wetlands to
tundra.
They were detected at 31 percent of shallow-water habitats,
defined as less than 1.5 meters deep, and over twice as common,
70.8 percent, at deep-water habitats, over 1.5 meters deep.
And the naive or the uncorrected estimate of frog occupancy
was 52 percent.
This figure shows just a brief overview of the results, with the
yellow locations being where frogs were detected, and you can see
frogs are detected right throughout all the areas that we sampled for
them. And the red was the areas where frogs were not detected.
Okay. Continuing with the results, based on the information
from the acoustic detectors, which, again, were set up to record the
calling patterns of frogs during the day, the calling peaked at about
1:00 in the morning, and then declined sharply by 5:00 a.m., and then
increased throughout the remainder of the day. So peak calling for
frogs was at 1:00 in the morning.
Next we estimated the detectability, and it was 60.6 percent if
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we visited a water body or wetland one time, increasing to
84.5 percent for two visits, and 93.9 percent for three visits. And I
would just say that most of the time we did two visits to the water
bodies.
So the occupancy in 2013, adjusted for that detectability, was
36.8 percent of the shallow-water habitat and 81.8 percent for the
deep-water habitat, with an overall occupancy of about 63.4 percent.
Now looking at the modifications to our study, the first one is
adding the Denali East Corridor option to the study area.
The second was to drop the opportunistic sampling of the
amphibian chytrid fungus. And that was done because in 2013 we
were only able to obtain seven frogs, and that tiny sample size was
unlikely to provide any useful results.
And the new modifications to the study since the ISR, as I
originally said, the Chulitna Corridor was dropped from the study
area.
And the steps to complete the study for 2014 are to conduct
the auditory field surveys, focusing on the areas that were not
sampled in 2013, including the CIRWG lands, the Denali East
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Corridor option, and the high-elevation areas that were not accessible
in 2013, generally above 2,500 feet.
Also to deploy acoustic monitors again.
And I'm happy to say that we were able to do all these things
mentioned on this slide in 2014.
Now just a quick look at the preliminary results from our 2014
data. We sampled 104 randomly selected wetlands and water bodies
from May 20 to May 29, and frogs were detected at only 8.6 percent
of the shallow water locations and 34.7 of the deep water locations.
So, a similar pattern as in 2013, but at much reduced levels.
The naive or uncorrected estimate of frog occupancy was
20.2 percent overall.
And we also conducted acoustic monitoring in 2014.
Unfortunately, we had some problems with the batteries which
limited the amount of data that we collected, but the overall patterns
of calling activity that we found were similar to those observed in
2013.
MR. LAWHEAD: Thanks, Todd.
MR. GILBERT: Okay. So the field collection is done on that,
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then?
MR. LAWHEAD: Yes.
MR. GILBERT: Okay. Any comments, modifications?
Anybody on the phone?
MS. MCGREGOR: Can you [2:31:20] (indiscernible)?
MS. BULLOCK: This is Sarah Bullock with the Bureau of
Land Management.
It's just kind of a question, but I was just kind of curious, no
modifications or anything like that, but do you have any -- like, any
hypothesis of why you had lesser -- a lot less detected in 2014 for the
auditory surveys compared to 2013?
Do you think, well, like, the mild spring may have done -- may
have affected it -- your survey period as compared to 2013 or --
MR. MABEE: I don't think it was the timing. I think we were
out there at the right time. I mean, when we got there frogs were
calling, and when we left frogs were calling.
I think it was perhaps the habitat, especially in the Denali East
Corridor in the higher elevations, that we were unable to sample in
2013. A lot of that habitat, you know, you've got old beaver dams
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and blown-out beaver dams, and it just didn't seem perhaps as
suitable for frogs, and it certainly wasn't the type of habitat where we
had seen -- where we detected frogs in 2013 or in 2014.
So my guess is perhaps it's a different habitat, less suitable.
MS. BULLOCK: Okay.
MR. GILBERT: That was a good question.
MS. MCGREGOR: So in the interest of time, the next three
studies have not been initiated, the next three studies on the agenda,
that is: 10.12, 10.20, 10.19. They haven't been initiated. They are
going to be deferred.
So if you guys could just really touch on the proposed
modifications to those studies, I think we can stay on track. I'm
not -- and open up for comments on any one of them.
MR. GILBERT: So there was no work in 2014?
MS. MCGREGOR: No work was conducted in 2014. There
wasn't any work conducted in 2013. We've been deferred to 2015.
There is no additional information, just the ISR, except for --
MR. GILBERT: Modification.
MS. MCGREGOR: -- the proposed modification, which is
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dropping the Chulitna Corridor. So if you guys -- there's just no need
to go into the objectives or components in all those aspects of these
studies.
MR. LAWHEAD: Correct.
MR. GILBERT: That's good, because they all fall in one
category.
MR. LAWHEAD: Okay. So we'll clip through these.
SMALL MAMMAL SPECIES COMPOSITION AND
HABITAT USE (STUDY 10.12)
MR. LAWHEAD: So basically this study, the small mammal
study, is a desktop-only study using the information -- a combination
of the information that was collected -- pretty detailed information
was collected -- in the 1980s by the University of Alaska Museum,
and to relate that information from the 1980s studies to the current
habitat mapping that's being prepared for the project, and also to try
and bring in additional information from small mammal
studies -- other small mammal studies that have been done since then
-- there aren't many -- and to incorporate some of the work that -- on
prey population abundance monitoring -- that the University of
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Alaska was doing as part of their terrestrial furbearer component, or
terrestrial furbearer study.
This information will -- as I mentioned, will be fed into -- the
results of -- and recorded in 10.19, the wildlife habitat mapping and
evaluation.
Okay. It's been deferred. It's not been initiated. The plan is to
do it next year.
We don't see any need for modifications except that the area
evaluated will differ on the basis of the corridor changes. And this
one is restricted to the corridors themselves. There's no additional
buffer area around them. So the Denali East Corridors
being -- Denali Corridors -- East Corridor is being added and the
Chulitna Corridor is being dropped.
And this pretty much repeats what I've already said.
MR. GILBERT: So this was always intended to be a one-year
study?
MR. LAWHEAD: Yes.
MS. MCGREGOR: It's a desktop study.
MR. LAWHEAD: Correct.
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MR. GILBERT: Okay. So not a lot of change.
Any comments, thoughts?
And this'll all be reported in the USR then? That's the final
place. Okay.
MR. LAWHEAD: Okay. Alex, do you want to take this next
one?
MR. GILBERT: Wildlife harvest analysis.
WILDLIFE HARVEST ANALYSIS (STUDY 10.20)
MR. PRICHARD: Okay. This is an analysis of existing
harvest data.
So the objective there, to summarize the past and current
harvest effort, harvest locations, access mode and routes for large
and small game from the data that's available.
Compare current harvest locations with data on seasonal
distribution, abundance, and movements of harvested species, again,
where that's available from these studies or other information.
And then provide harvest data or interpretation of harvest data
for use and analyses for the recreation and subsistence resource
studies.
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Okay. And so the components are compilation and analysis of
the existing data, which is Fish & Game harvest data base records,
Fish & Game game management reports, trapper questionnaires, the
small game outlook and harvest surveys, review of ADF&G and
Fish & Wildlife Service subsistence surveys and harvest reports, and
interviews with regional biologists, so trying to get all the available
data on harvest in the area, and then compare that -- those data --
with harvest patterns -- or compare those data on harvest patterns
with the current distribution of game mammals and birds and
development plans.
So it was deferred until 2015. So -- and it can be completed in
one year, so by deferring it will actually look at all the previous data
that's available.
MR. LAWHEAD: Yeah. And I should mention here that we
did an initial analysis of this data in 2012 as a tech memo, which
looked at most of the historical data that were available, and that
gives you a good idea of what the final product is going to look like.
So this analysis is a matter of adding additional data that's
accumulated since then into that same analysis.
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MR. GILBERT: Sure. Go ahead.
MR. MILLER: This is Sterling Miller again. I haven't
reviewed this study, but this makes an off-the-cuff recommendation
for a study modification.
You heard Earl say that -- Earl Becker say -- with regard to the
bear studies, the black bear, the brown bear studies, that the reason
some of those areas were lighter than other areas were because there
were fewer bears there.
And I strongly believe that that's not true, and you can -- even
though harvest data are an imperfect reflection of bear abundance, if
you were to look at every bear that's killed, black bear or brown bear,
is assigned to a bear harvest management unit, so you know exactly
where the bears are taken. So my suggestion is that you look at the
harvest data and develop a harvest density map equivalent to what
we saw for proposed bear density.
And it's my guess that the areas where Earl's study was
showing very low black bear and brown bear density, will, in fact,
come out very high in terms of harvest density. And that shows at
least an indication, although not proof, because access and other
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things reflect harvest density, but very strong indication of whether
or not Earl's assertion that density is lower in those areas is correct or
not. So that's a suggestion, that you look at bear harvest density in
the large carnivore study area.
MR. GILBERT: Sure. Mark?
MR. BURCH: Yeah, that's an interesting perspective. Again,
our concern would be the season of the harvest versus the season that
the surveys were done in. I don't know what your perspective is on
that.
MR. MILLER: Well, all those areas have spring seasons, so
you can look at harvest density in the spring season, if that was a
concern.
But, in fact, bears don't move all that much except to salmon
streams, and so you do get long-range movements to salmon streams.
But other than that, most of the movements within a bear's
home range are, you know, small compared to the huge size of that
large carnivore study area. So you should be able to get something
by lumping spring and fall seasons.
In fact, I did that in my -- 1993, I published a Fish & Game
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technical report called “Bear Management in Alaska, a Statewide
Management Overview,” in which I looked at harvest density in
various areas. Because I was trying to be interested in whether or not
the 20A harvest density, where they claimed the bear population had
gone down, was higher than in the 13E study area, where I was
studying, and they were harvesting bears at a much lower density in
20A than they were in 13E.
MR. LAWHEAD: Okay. Alex?
MR. PRICHARD: Do you want me to respond to that or --
MR. LAWHEAD: No. Comment noted.
MR. GILBERT: Is there anybody else, anybody on the
phone?
MS. MCCLURE: Hi, this is Lauren McClure, contractor for
FERC.
Alex, I had a question for you. I just wanted to confirm that I
understood the slide correctly.
Will the results of the harvest analysis also include bird
species?
MR. PRICHARD: I don't think we have those data, other than
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there's a small-game outlook.
MR. LAWHEAD: For upland game birds.
MR. PRICHARD: And [2:42:23] questionnaires. I think it's a
very coarse level.
MR. LAWHEAD: Yeah. It includes upland game -- upland
game birds, but not waterfowl.
MS. MCCLURE: And that was probably figured out during
the development of the study plan, to not include waterfowl?
MS. MCGREGOR: It just has to do with the reporting.
MR. LAWHEAD: Yeah. There's no good way to get at it. It's
not part of a reporting network.
MS. MCCLURE: Thank you.
MR. GILBERT: Okay. Well, we have one more to do, and
then we're going to take a break and try to keep on track here. We're
not far.
So this is another study that was deferred, right? Habitat?
MR. SCHICK: Yes.
MR. GILBERT: Terry, you're going to do this one, correct?
Okay.
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EVALUATION OF WILDLIFE HABITAT USE (STUDY 10.19)
MR. SCHICK: Yeah. So this is evaluation of wildlife habitat
use. This is all a desktop study, depends heavily on the wildlife
habitat mapping, which we'll talk about after the break.
How can I advance this slide?
Objectives. We will prepare categorical rankings, high,
medium, low values for all of the mapped habitats for bird and
mammal species in the project area.
Next. This is to be based as much as possible on
project-specific data, overlaying those observations on the mapped
habitat types. When that's not possible, we'll use scientific literature
on habitat use to supplement that project-specific information.
Next.
Variances. It's all been deferred. The study can't be completed
until the mapping is done for Studies 11.5 and 11.6, downstream of
the proposed dam, and when wildlife study survey data are also
available.
Next.
No work has been initiated on this.
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Modifications. Okay. The four-mile study area buffer has
now been reduced to a two-mile buffer. We'll discuss that after the
break, under Study 11.5.
But this mirrors the study area for Study 11.5, so because it
went to two there, it's going to be two here.
We have the new Denali East Option Corridor. We will not
select bird species for analysis, as described in the RSP. We will
rank habitat values for all bird species that have been recorded in the
project area.
Next.
The study area is very hard to see, but it goes all the way to
project river mile 29.5, the southern end of the riparian vegetation
study area, and then the full two-mile buffer study area around the
project area components in the upstream area, and includes the new
Denali East Option Corridor.
Next.
Chulitna Corridor has been dropped.
The steps to complete the study, they're all described in the
RSP. Select mammal species of concern and evaluate all bird
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species. Project-specific literature, or specific survey data -- excuse
me -- project-specific survey data will be the main focus, scientific
literature will be used when the survey data are not adequate.
Next.
MR. GILBERT: Okay. So not much change in that study
other than the --
MS. MCGREGOR: Study area.
MR. SCHICK: Yeah. Really, the study area changed, but
that's -- it's going to follow exactly the changes in the habitat
mapping study area. The only real changes we've cited will be
skipping the selection of bird species, which is often fraught with
problems, given how many birds there are and how many different
opinions about which ones should be selected. We'll just do them all.
And people can select those species of interest, in terms of
assessing habitat use and loss, when the license application is
prepared.
MR. GILBERT: Any comments? Federal, state, others?
MR. LAWHEAD: Anyone on the phone? All right.
MR. GILBERT: Good. Thank you.
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MR. LAWHEAD: It's break time, right?
MR. GILBERT: Yeah. We're going to take a break, and we'll
try to start back right at the top of the hour, 3:00 again, so we can get
through all of Terry's four studies.
So we're putting you guys on mute, so everybody try to be
back at the top of the hour, 3:00.
(Off record.)
MR. GILBERT: So let's get started again, to make sure we
can go all through these and make sure there's time for any questions
or comments. That's the most important thing.
Okay. So we're going to go through studies ABR -- the
botanical studies, first one wildlife --
MS. MCGREGOR: Can we wait one second? Is Fish &
Wildlife Service gone? Did Phil leave?
MR. MILLER: Phil Brna left.
MR. GILBERT: Okay. So we are a lot smaller group here,
but we're going to get through the botanical studies.
MR. SCHICK: Okay. Are we ready?
MR. GILBERT: Uh-huh.
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VEGETATION AND WILDLIFE HABITAT MAPPING
STUDY IN THE UPPER AND MIDDLE SUSITNA BASIN
(STUDY 11.5)
MR. SCHICK: Okay. This is Study 11.5, Vegetation and
Wildlife Habitat Mapping in the Upper and Middle Susitna Basin.
We referred to this study several times today.
The objectives basically are classify, delineate, map existing
vegetation and wildlife habitats in those areas that could experience
direct impacts and indirect impacts on (on does not make sense, s/b
from) the proposed project.
The ultimate goal for the wildlife habitat mapping is this map
will be used in assessing, via Study 10.19, which we just talked about
before the break, to assess overall habitat loss and alteration impacts
for bird and mammal species.
UNIDENTIFIED FEMALE: (Indiscernible - interference with
speaker-phone). [3:03:28]
MR. SCHICK: Components --
MR. GILBERT: Somebody needs to mute their phone unless
you have a comment, because we think you have a comment.
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MR. SCHICK: Components are pretty straight forward.
We're developing mapping materials from previous historical data
from the 1980s, field surveys to ground truth the aerial imagery we're
using, and what we're calling ITU (Integrated Terrain Unit) mapping
efforts, a multi-variate mapping of different landscape variables,
including vegetation.
This study is being conducted in close coordination with 11.7,
which is the wetland mapping study in the same study area, which
Wendy Davis will talk about here in a moment.
Variances, there were none for field studies or the mapping
effort for this study, from what was described in the RSP.
Summary of results, in the ISR in 2013, a total of 916 plots
were surveyed. 619 of those were full plots. 297 are what we call
rapid map verification plots, where we collect a subset of data used
to validate previous image signatures that were already sampled with
full plots.
The ITU mapping effort is ongoing, expected to be completed
in 2015. And we're recording a set of different landscape variables
for this study and the wetland mapping study. Here's the full set.
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Alaska Vegetation Classification Level IV vegetation types;
physiographic types; surface forms; disturbance type, when
applicable; and then these two specific to the wetland mapping study,
NWI wetland class; and hydrogeomorphic (HGM) wetland class.
Here's the survey area for 2013. As we discussed a number of
times for other studies, the Gold Creek Corridor and portions of the
reservoir were not sampled in 2013 because we didn't have access to
CIRWG lands. We have that access now, and we'll sample those
areas in 2015.
There's no indication that we need to sample these areas in two
years. All we're doing really is tagging photo signatures, image
signatures, with ground-truth data to help support the wildlife habitat
mapping and the vegetation mapping efforts.
This map, you really can't see the map polygons at all. This
was in the ISR. This is an example of rather detailed
alpine -- subalpine mapping, and it's an example of how those data
are aggregated from the original mapping over here on the left to
more broad-scale wildlife habitat types on the right. And you'll see
much more of that in the USR.
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Summary of results since the ISR, there's been no additional
field surveys. There were no field work done for this project at all in
2014. The second year of surveys is postponed to 2015. The ITU
mapping, however, has continued.
Proposed modifications, originally there was a four-mile study
area buffer for this study. We reduced that to two miles, for a
number of reasons. This -- the two-mile study area buffer matches
the study area for 11.7 for wetlands mapping, and also for Study
10.16, landbird and shorebird surveys, largely point-count surveys.
The two-mile study area buffer is still pretty darned big.
That's two miles on either side of the edge of the project corridor,
which is a buffer itself. And we ran this by wildlife researchers
working on the project, and the conclusion was that two miles was
adequate to assess local-scale project effects on wildlife habitats
from both direct and indirect impacts.
And we have also added the Denali East Option Corridor, and
a two-mile buffer around that.
This is a depiction of the new study area with the Denali East
Option Corridor here in red and going forward we will be mapping
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that corridor also. While we have not been mapping, as of early in
2014, in the Chulitna Corridor, we do still have data for the Chulitna
Corridor, however, both ground data and mapping data.
The Chulitna Corridor has been dropped.
Current status, the first year of field surveys --actually we
started this in 2012, so we have some data for 2012. We also have
data for 2013 for field surveys.
In 2014, we have the two modifications described above, and
we implemented the ITU mapping work and it's ongoing. And we'll
continue that mapping in 2014/2015.
So in the next study year, we will do the final field survey
work to support the ITU mapping effort. We'll finalize the ITU
mapping in the first part of 2015. A preliminary set of wildlife
habitat types was developed for the ISR. We'll finalize those with
input from the wildlife researchers working on the project, and in
coordination with the study team for the riparian vegetation study,
which is being conducted downstream of the proposed dam site.
And that's all I have.
MR. GILBERT: Okay. Good. We don't have Fish & Wildlife
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Service, but anybody else? Questions?
MS. WOLFF: I have a quick question. This is Whitney with
Talkeetna Council.
Does the 2012 data -- did you use the two- or the four-mile
buffer?
MR. SCHICK: 2012 I think was done with the four-mile
buffer.
MS. WOLFF: Okay.
MR. SCHICK: Yeah. That was the original buffer.
Actually --
MS. WOLFF: Okay. But you started -- go ahead.
MR. SCHICK: Actually, I think 2013 data were collected
with the four-mile buffer also. So you will see some points that may
be outside of the actual mapping area. That's okay. That still
provides us data that are linking ground variables to the image
signatures. It's not like it's data that's not going to be useful.
MS. WOLFF: Okay. Good. That's what I was hoping you'd
say.
MS. MCGREGOR: Another question, comment back here.
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MR. GILBERT: Oh, yeah, sure.
MR. MILLER: Sterling Miller again. I'd just like to put down
a marker once again for what we discussed earlier about extending
the vegetation studies and habitat studies more broadly so that
those -- some ability to analyze habitat use by animals with GPS and
other kinds of collars is possible beyond a wider area.
Now, you did say that would be a lower level of varied
classification, or higher level, I guess, a less precise, less detailed.
But some level of analysis at a wider geographic scope, where it's
pertinent to the analysis of habitat utilization by some of these
radio-collared animals.
MR. SCHICK: Yeah, absolutely. We will be able to do that
by cross-walking the fine-scale habitat mapping that's done within
the two-mile buffer to a more coarse-scale map outside of that area.
Probably Ducks Unlimited mapping is maybe one of the most
suitable for that area, which Kim has used in her plot allocation
process for the moose GSPE surveys. So that's definitely a
possibility.
MR. GILBERT: Okay. Anybody else on the phone or
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otherwise?
MS. BULLOCK: Sarah Bullock, BLM.
I assume the reason why you're deferring the field surveys to
2015 was because of issues earlier in the year with the CIRI -- or the
-- or let’s just ask, why were they deferred to 2015 and not done in
2014?
MS. MCGREGOR: Do you want me to answer?
MR. SCHICK: Yeah, why don't you respond to that?
MS. MCGREGOR: Okay. So holistically across the entire
environmental program, we had limited funds. We didn't get all of
the funding that we needed to carry out the 2014 work, which is why
we ended up with a deferment and splitting the ISR into what we
provided in February versus what we provided in June.
So we prioritized study and data collection efforts across the
entire program to determine how best to allocate those funds and still
stay as close to on schedule as we could with filing the license
application. So some of these studies had less data collection.
Basically anything that wasn't biological and seasonally tied or we
had to collect two years of data or collect data from the winter
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through the fall, something along those lines, became a lower
priority.
The other issue is that, particularly for the first two botanical
studies up there, 11.5 and 11.7, they're really large study areas. So
while the data collection component didn't occur in 2014, these guys
did continue the mapping of and the interpretation of the aerial
images, which is incredibly time consuming.
MS. BULLOCK: Okay. Thank you.
MR. GILBERT: Another question?
MR. SCHICK: Anything else?
MR. GILBERT: So now I guess we get Wendy. She's been
quiet the whole time. Three studies.
MR. LAWHEAD: Just scroll.
MS. DAVIS: Just scroll? Okay.
MR. LAWHEAD: Change your slides.
WETLAND MAPPING STUDY IN THE UPPER AND
MIDDLE SUSITNA BASIN (STUDY 11.7)
MS. DAVIS: Okay. So this is the wetland mapping study,
and it's going to look really similar to the study we just heard about.
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Basically there are two main objectives, and the main one
obviously is to classify and delineate a map of the wetlands within
our study area boundaries.
And then the second objective is essentially to do a functional
assessment of the mapped wetland types. So once we get the map
finished, we need a functional assessment on the classification efforts
that we've completed.
So the components of this project are obviously field surveys
and wetlands mapping.
Then we've got a multi-variate wetland mapping process that's
ongoing, and it's a concurrent effort that goes along with the wildlife
habitat mapping, multi-variate mapping that refers to basically what
Terry called ITU mapping. So it's just referring to all the different
attributes that we use when we map polygons.
And then the functional assessment, which yeah, we covered a
sample -- initial sample functional assessment in the ISR. And yeah,
like I said, this is being run concurrently with the wildlife habitat
mapping.
We have no variances on this study.
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And this is the same map as Terry showed. So all of the
wildlife habitat field plots are also wetland field plots. And his
response to that previous question, also we'll be using all of the plots
that we sample, even though they're maybe outside of the two-mile
boundary, to apply to those signatures that we encounter inside the
study area. And this is missing plots obviously, on CIRWG lands.
All right. So our results, you know, obviously we're still
mapping. And these are the same plots that Terry mentioned, so
you've got a total of 916 plots. 619 of those are full plots, and 297
are the verification plots.
The full plots are the -- include a lot of extra information, but
it has the full Army Corps wetland delineation form included, and
then a number of variables for the functional assessment, as well. So
yeah. So mapping is ongoing, to be completed in 2015, and
we -- like I said, we've got some example maps and some attributes
recorded on each polygon in the ISR.
The first three attributes listed there, the NWI code, the HGM
classes, and the Alaska vegetation classification, are the ones that are
the real key ones that we aggregate to try and classify wetland types,
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but we do use physiography, surface form, and disturbance type to
help, you know, inform the decisions.
And here's our -- one of our examples. We performed a little
spot functional assessment on this wetland, and this is just an
example of what the wetland mapping would be like. The attributes
on here are really teeny tiny, but that's the NWI classification system.
And these are slope wetlands that are forming in the trough
formations on the south face of the -- yeah, the south face of the
Susitna Basin.
And all right. So we haven't done any more field surveys.
We're just mapping, so we don't really have any results since the ISR.
We don't really plan any modifications except for that, as
mentioned before, there's the addition of the Denali Corridor East
option, and we've got that added to our study area and have started
mapping.
And this is the same map that Terry put up for the wildlife
habitat area, though it shows in red there the new Denali Corridor
option. And the little bit -- the little bit that's cut out that the riparian
people are mapping up here along the river. And then our map will
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just join in with their map in the end.
And so current status, you know, we completed field surveys
in 2013, and we also had a few points collected in 2012. The
modification in 2014 to add the new part of the study area, and we
were just continuing mapping. And I guess that's the main story,
mapping, mapping, mapping.
Yeah. So the steps to completion. We have still another field
campaign planned for 2015, and we will be selecting points on
CIRWG lands where we just don't have any plot density at all. And
additionally we would collect points outside those areas if we might
have found we don't have enough information to map the photo
signatures that we've got, so I guess the ideal situation would be
finish the mapping and then go out and kind of ground-truth with the
2013 so that we can keep on schedule. Yeah.
And then our -- all of our attributes will get aggregated into a
project-wide classification, which includes hopefully a manageable
number of wetland types, and we feed those in to the wetland
functional assessment.
We have a task still ahead of us to revise some of the model
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variables used in the Magee wetland functional assessment to make
them more relevant to the study area.
And we also have the task, once these other studies that we've
identified that we're sharing data with, once we get information from
them, we have the task of kind of ameliorating our functional
assessment to have sort of regionally specific values for the
functions. So we're going to be looking for abundance of -- and fish
habitat studies, all of the wildlife studies, and to use information
from the recreation and subsistence studies, and those last two are
going to be used to inform the two functions that aren't part of the
Magee method right now, which are consumptive uses and
subsistence.
Yeah. And then all this is kind of an iterative process, but we
also have close to a final set of wetland types now, but all this will be
run through the model and we will be kind of refining our
classification and finally the final set of wetlands that go into the
final functional assessment will be called wetland functional classes,
and that's still ahead of us.
And that's -- that's it.
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MR. GILBERT: Okay. Good. So not many modifications.
I know we have kind of a small group, but any thoughts,
questions? Sound reasonable?
How about on the phone? Do you guys have any questions for
Wendy?
That's good. Okay. Let's keep going.
MR. SCHICK: This is you.
MS. DAVIS: Oh, it's me. Okay. Rare plants.
RARE PLANTS (STUDY 11.8)
MS. DAVIS: Oh, it's me. Okay. Rare plants. Okay. Right.
So study objectives for rare plants. First of all, we were tasked
with identifying habitats in the project area. And this is just the
project area, the buffer corridors that we were provided with. So
identify habitats that are likely to have rare vascular plant species.
And perform field studies, search those habitats within a
project area, map the locations, and estimate population sizes if we
do find any rare plants.
So the components. Initially we kind of -- desktop portion of
this, where we selected focal species and habitats, and to do that, we
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used the Alaska Natural Heritage Program database and scanned for
possible rare plants in kind of a broad region surrounding the project
area, so that we could try to be as inclusive as possible.
And when we were doing the field work, they focused on that
list of species that were -- that fell within the S1, S2, and S3 rankings
at Alaska National Heritage Program rankings. So if you're not
familiar, Heritage Program has this ranking system that goes from S1
to S5.
And S1 to S3 are essentially all the plants that are deemed rare,
and after you pass a 3, it's really not rare anymore. And using S1
through S3 is still a very inclusive list.
Yeah. So then we have surveys. And this one is another study
with no variances from the RSP.
These are -- so this is the smaller contracted study area
corridors. And the blue transects are planned but not yet surveyed,
and the yellow transects were surveyed in 2013. So they got a pretty
good coverage with the transects set up like this. They had relatively
long transects that they would walk on during the day, and were able
to cover a large number of habitats and scan for as many species as
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possible.
So I've mentioned, field surveys were conducted. They did 16
transects and they were pretty well distributed around the study area.
And they found two rare plant species, Vicia americana, which
is an S2, and Eriophorum viridicarinatum was an S2S3.
The Vicia was found right in the helo-pad right at Gold Creek
camp, right within the first five minutes of Tako Raynolds entering
the field study site. And Eriophorum was found in a natural bog type
area.
There were other rare taxa found. I think I believe they're on
the riparian study, and so those are taxa that are going to be targeted
the next time they go out to complete this field survey.
So they completed the ISR and nothing more since then.
There's no plans to modify the study plan. And as with all of these
botanical studies, they've added the Denali Corridor East option, and
so we'll identify some transects within that corridor for the follow-up
field survey.
And this is -- so this is the map that's the smaller study area,
but showing the fully added piece in shaded red. We've already got
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some coverage in general areas along there, but they'll be focusing on
that, to add new areas in this [3:29:02].
All right. So they completed their field surveys. There's no
variances. They were pleased to cover a wide range of habitats and
found two rare species, and would be targeting the CIRWG lands and
the new areas for field studies in 2015.
All right. So to complete this study, they have to go
back -- well, probably won't have to go back, but if there are any new
habitats that are in the new Denali East Corridor area, they have to
go back and maybe try and discover if there are any new target
species to look for.
And same thing, repeat the field survey, find rare plants and
estimate population size. And they're still, like I said, no variances to
show it's described in the RSP.
MR. GILBERT: Good. No variances, no mods. Any
thoughts, comments?
MS. BULLOCK: Sarah Bullock with Bureau of Land
Management.
I'm not quite sure if my question really fits in the purview of
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rare plant studies, but I know that BLM has a list of sensitive species,
and I wasn't for sure -- I don't think those are quite equal, but do
those -- does the rare -- because I know that on the Heritage site, it
has a whole list of how they're ranked with both Fish & Wildlife
Service, their internal rankings, and BLM sensitive species, and I
was just kind of curious if BLM sensitive species kind of aligned
with --
MS. DAVIS: Yeah. The Heritage Program tracks all the
different classifications. And yeah, I don't think there was anything
that was on the sensitive -- the BLM list that didn't fall within our
broad category of potential rare focal species.
MR. SCHICK: I think that almost has to be true.
MS. DAVIS: Yeah.
MR. SCHICK: We have included the S3 species, which is an
in between class -- they call it vulnerable. It's not really rare yet, so
we threw the net a bit broader to get S3, S2, and S1. So I'm guessing
that all of the BLM sensitive are in there.
MS. BULLOCK: That was kind of my guess, too, but I just
wanted to put that comment out there and just, you know, check on
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it, I guess.
MR. LAWHEAD: There's 13 species in the BLM sensitive
list.
MR. GILBERT: How many?
MR. LAWHEAD: Thirteen.
MR. SCHICK: And we had a list of 39 target, S1, S2, S3
species, I think, within a big broad search area. It was actually --
MR. GILBERT: Sounds like --
MR. SCHICK: Well, sub-watershed survey area that we used.
MR. GILBERT: If they cull that out in the reporting to make
sure they’re clear.
MS. BULLOCK: It would be good if you did -- I mean,
because you say you used the Heritage Program program’s list, but it
would be also good, if one of those two rare species were also BLM
sensitive species, to point that out, as well. Because a lot of your
studies here coming up are what you plan to do in 2015, look to be in
a lot of BLM lands that would be --
MR. LAWHEAD: Oh, I found another page. Oh, there's a lot.
MS. BULLOCK: Well, that's just in the whole state, so those -
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- there’s a very small subsection that qualify for this particular area.
MR. GILBERT: Okay.
MR. SCHICK: One more, right?
MR. GILBERT: Sure. Invasive.
INVASIVE PLANTS (STUDY 11.9)
MR. SCHICK: Okay. So this is invasive plants, similar to
rare plants in terms of a study effort, but it's a totally different group
of plants.
The objectives here are to locate, really, sources of invasives
that could be transmitted into the project area during the construction
phase or the operations phase. So the idea is to look for current
populations of invasive species, map their locations, and estimate
population sizes, and also assess ecological threat for the invasive
species located.
So the components were field surveys for invasive species.
And as you'll see, the sites surveyed were disturbed areas in 2013.
They really weren't even in the project area. They were surrounding
it. And then conduct an ecological risk assessment for each of those
invasives to assess possibility of spreading into the project area.
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There were no variances for the field surveys and risk
assessments for invasives in 2013.
Field surveys in 2013. 107 sites were surveyed in late August.
These were possible source areas, disturbed areas along the Denali
and Parks Highway, pullouts, and regularly used or ORV trails
leading into the project area.
28 of those 107 sites were revisits to locations where invasives
had been recorded previously by the first set of surveys by the
Alaska Natural Heritage Program.
Invasive species were found at 98 of the 107 sites sampled.
And across all of those 107 sites, 31 invasive species were recorded.
So this is a list of the 15 species with the highest invasiveness
ranking, so the invasiveness ranking is there on the right. Melilotus
alba, sweet -- or white sweetclover, has the highest invasive rank in
the set of species that we located. I think it may be the highest in the
set of invasive species known in the state actually. But that species
was only recorded at seven sites.
Conversely, another species of concern, because of its
capability to spread, is Hordeum jubatum. Many of you have
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probably seen this species. It has an invasiveness rank of 63, it was
found at 50 sites, approaching half of the sites.
You've probably seen all of these species before along
highway right-of-ways in Alaska.
So the preliminary ecological risk assessment findings in 2013,
given the current data collected in the Parks Highway and Denali
Highway corridors, are that the risk for invasives being transported in
to the project area is relatively low. And that's primarily because of
the bottom bullet here. This concerns these two species in particular.
But many of the other species were found at very low cover values
also. Cover values for the two species were less than 1 percent at
each site, or trace values, or low 1 to 5 percent cover.
Of the two species that are probably of most concern, out of
the 31 species found (Hordeum jubatum and Melilotus alba),
Hordeum jubatum is able to colonize a lot of different habitats from
wet sites to very well-drained, gravelly substrates, and silty soils. It's
easy to get around. And it also gets stuck in clothing very easily, so
it's very transmittable.
Melilotus alba is considered highly problematic. It forms
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dense stands on river bars and disturbed areas, and there's some
indication that it may have negative effects on colonizing native
Alaskan species, as well.
Summary of results since the ISR. No additional work has
been done since 2013 in the preparation for the ISR.
Modifications. None really are needed for this study. The
study area has changed, again, because of the addition of the Denali
East Option Corridor, so we'll have to add some additional sampling
in 2015 along the Denali Highway to cover the area where the Denali
East Option Corridor merges with the Denali Highway. And that's
basically it.
And that's a map indicating here's our 2013 study area, along
the Parks Highway and Denali Highway Corridor, so we just need to
extend this out a short ways here in 2015.
Current status. 2013 field surveys were completed as described
in the RSP. There were no variances. Like most of the other
botanical studies, no field surveys were conducted in 2014. The final
surveys will be conducted in 2015.
And the preliminary ecological risk assessment was conducted
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as described.
So steps to complete the study. As I mentioned, we'll go out
again in 2015 and sample disturbed areas in and near the project area.
On the target list right now are additional sampling of the Denali
Highway, as I just mentioned for the Denali East Option Corridor,
and also look at three of the primary lodges that are being heavily
used during the research phase of this project (Stephan Lake and
High Lake lodges and Gold Creek camp) to assess invasiveness
presence and population sizes in those areas. And at the
recommendation of the U.S. Fish & Wildlife Service, to look along
the Alaska Railroad corridor right-of-way, pending adequate permits
to do so, where the railroad would come into close contact with the
Gold Creek Corridor.
Again, we'll review existing data in the Alaska exotic plants
information clearinghouse database, which is maintained by the
Natural Heritage Program, and aerial imagery to identify any
additional sites -- any additional disturbed sites to help guide those
survey efforts in 2015. And we'll conduct a final risk assessment for
those species found in 2013 and '15.
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And that's it.
MR. GILBERT: Wow. Okay.
MS. LONG: Hi, this is Becky Long. I have some comments.
MR. GILBERT: Sure, Becky. Go ahead.
MS. LONG: Just basic ones.
First of all, I think you guys did a good job on this study. And
I'm also glad to know that the current risk assessment overall is very
low, that there's no crisis of invasion of those invasives.
I think everybody will all agree that early recognition of
invasive plant species can preclude [3:42:13 herbicide use, and that's
my interest in this study, is to make sure that invasives don't happen,
so that there's an excuse for herbicide use.
On Part A, page 6, I'm just a little bit confused about the
statement. It says, you know, that -- well, all three -- alternative
corridors originate at Parks Highway or Denali Highway, but now
the Chulitna is not one of them.
But I just was confused, because they don't really touch the
Parks Highway. I mean, Gold Creek is approximately eight miles
away from the Parks Highway, Chulitna is approximately 5.5 miles.
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So I was a little confused by that statement.
But are you saying that invasives along the Parks Highway
could affect those routes, even though they're not directly connected?
And then I'll just finish up, that when we had the informational
meetings, AEA this spring in May and June, I think BLM was
present and they really were interested in the possibility of invasives
being spread by just the actions of the licensing studies, and hoping
that there is best management practices that are going on.
And that's it.
MR. SCHICK: Okay. Those are good sets of questions.
With respect to the Parks Highway, Denali Highway
Corridors, and the railroad, we are not entirely sure how construction
materials would be transported to the project area. It kind of depends
on which corridor is finally selected.
So we're trying to cover the bases, and that's -- I think was the
genesis of the recommendation, to try to do some sampling along the
railroad corridor because the railroad corridor could be, in fact, used
during the construction phase.
I could see how you may be a little bit confused about that
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sentence in the ISR, because the Gold Creek corridor doesn't actually
connect with the Parks Highway. It connects with the railroad
corridor.
And then in with respect to best management practices, there
will be, I believe, a -- what are we calling it, Janet, an invasives
management plan that will be prepared probably as part of the license
application?
MS. KIDD: Yeah. This is Janet.
I think the comment was made about best management
practices going on actually right now, with respect to current studies
that are going on, and it's a good question.
And I don't know if there's really been a concerted effort to
make sure people are wiping off all their shoes before they come off
the planes that are entering into the study area.
We do know that at the field camps, like -- like at Stephan
Lake Lodge, because there's just a lot of historical use there, there
were some invasive things, dandelions and things of that nature that
we did find in 2012. High Lake lodge, I'm not sure. But just, you
know, this is something -- another concern that has, to our
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knowledge, not been brought up before.
And probably we should be making more of a concerted effort
to make sure that we're not actually, you know, introducing invasive
plants as part of the study for this project.
MR. SCHICK: Yeah. It's a good point. I think a lot of
invasives are actually transmitted by movement of large machinery
and that kind of thing during construction, but it is a good point, and
it's something that we can consider as the study moves forward.
MS. KIDD: Another follow-up comment I wanted to make
with respect to the fact that there's no direct access from the Denali
Highway into the project area.
And what we did try to do, though, was look at trails that do
come off the Denali Highway into the project area, and so that was
what we were looking at right now, at this stage, is are there potential
corridors to transmit invasive plants from strictly ORV traffic?
And that was one of the things that we thought was
encouraging is that we really -- even when we walked kind of well
into these trails, we really didn't see a lot of invasive plants really
right -- they pretty much were right, you know, confined to the road
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itself, or maybe the gravel bed next to the road.
But as soon as you started to get into the sort of native soil, the
silts, even associated with the trails, you know, we just did not see a
lot of movement of invasive plants into those ORV trails.
MR. GILBERT: Okay. Sterling.
MR. MILLER: Yes. I just have a brief comment, and that is, I
now live in Montana, and it's a place where a few years ago --
MR. SCHICK: Did you wipe your shoes before you got off
the plane?
MR. MILLER: That's right. Where a few years ago, the
people dismissed the dangers of exotic plants, and much to our
current dismay invasive plants are now quite common.
And so I like the idea of your -- I mean, it affects wildlife
habitat and all kinds of things. So you know, paying attention to this
is well worthwhile.
And I like your idea of studying current penetrations, like,
along the railroad corridor or others like that, and doing some
transects off -- if you're surveying, you know, exotics in the
immediate vicinity of these penetrations, you know, going off the site
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a bit, you know, with right-angle transects, might be worthwhile to
see how -- you know, see how -- because right along the actual
corridors, you have disturbed habitat for the plants, which many
exotics find congenial because they're pioneers, whereas maybe a
little off, they're not.
But if you find some exotic plants that are off in non-disturbed
habitats, that have spread there from the disturbed habitats along the
penetrations, that's quite a cause for concern.
So I know you know all this, but I just thought I would
mention it.
And at the very end, when all these other -- I just have a few
comments which I think pertain to all species. It'll only take me
about two or three minutes.
MR. GILBERT: Okay. Sure. Which we may be at.
MS. BULLOCK: I have a question. Sarah Bullock, Bureau of
Land Management.
Could you turn back to the figure with the study area on it
there?
MR. SCHICK: That one?
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MS. BULLOCK: Yeah. I was just kind of thinking about,
have you or either -- since this is just an invasive plant study, is this
including aquatic invasives, as well? Have you looked at any, like,
lakes that are -- you know, that planes with floats could possibly get
in, or have you identified any, you know, Super Cub landing strips
within those corridors?
Which I don't -- I mean, could you find them? I don't know.
But that could also be another potential area for exposure to invasive
plants.
MR. SCHICK: Yeah. No. It's a very good question. The
answer is no. We have -- this study is limited to terrestrial invasive
plants.
MS. BULLOCK: I know it's just the road corridor, but I'm,
like, there's a lot of guiding out there.
MR. SCHICK: Yeah. But aquatic invasives are an issue.
They're a growing concern in Alaska. But this study is not designed
to address that.
MR. GILBERT: You do have the lodges you mentioned that
aren’t on the map.
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MS. MCGREGOR: Yeah. Stephan Lake isn't on that map,
within the study area. It's on the map. It's just not within the study
area.
MR. GILBERT: Right.
MR. SCHICK: Well, the study area is a very loosely defined
thing for the study in particular, because really its disturbed spots
where we decide to sample. So you know, if we find disturbed spots
along the existing corridors, we may go and sample those.
But the likelihood of finding disturbed sites there is remote.
They're basically along the railroad corridor or the road corridor.
MR. GILBERT: Those are the main places.
MR. SCHICK: And then you've got them at various lodges
where people have been flying in for years.
MS. BULLOCK: I recognize the difficulty of my request.
MR. SCHICK: Well, that's -- that's a different study really. If
you're going to study aquatic invasives, you'd want to start at Lake
Hood, the float plane base in Anchorage, presumably.
MS. KIDD: And I guess I will say that, it isn't obviously the
target of the wetlands and vegetation mapping studies, but we are
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asking our field crews to make observations, that if they do find any
invasive plants, especially with the lakes or waterways that are
included in some of our survey plots, and if we did find something
there, then we would probably make more of an effort to study that
area.
You know, particularly, if we knew there was a lot of human
access, you know, recreational activity, because it’s a huge study
area. It would be challenging for us to know which lakes are
potentially to be used by floatplanes, and it's a big concern. It would
be pretty hard to narrow the scope I think for that.
But we are asking, you know, all of our folks, and then people
that are doing the riparian study downstream, where there actually is
quite a bit of boat traffic, I'm asking them to make note of species
that they know would probably be not -- you know, not native.
And an important distinction to make here, too, is invasive
versus non-native. And we do have non-native species around, but
they're not all considered invasive. Some of them have been here for
a long time, maybe because of historical mining activity or other
things, but important distinctions are made there where invasives
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really do have an ecological impact potentially on the native plant
populations as opposed to only being non-native.
MR. GILBERT: Okay. Anything else on invasives?
And then we'll go to your comments, and then Betsy has a few
remarks, and then we'll probably close it up.
MR. MILLER: This is Sterling Miller. I want to thank
everybody for the opportunity to make these comments. I found
many of them interesting and illuminating and pertinent.
When I designed my comments, I had a bunch of comments
that were specific to specific studies, and then I had some comments
which were sort of general to all studies. And to avoid repeating
those general comments in each specific study, I appreciate the
opportunity. I just have four things to comment on that pertain to all
studies.
One of the things is that it's clear that in all of the -- that the
decision was made by the Energy Authority not to list the authors of
the work in the studies, and I wanted to put down a request that you
actually list the names of the people who did the studies and did the
analyses and prepared the reports. The credentials and credibility of
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the individuals doing that work is pertinent to evaluating how
credible the studies are.
I'm not saying that any of the studies are not credible, but just
that I think listing the people involved is a good idea, just to establish
the credibility of the reports themselves.
The other -- another comment is that -- and I've touched on
this -- been touched a little bit -- I think it's unfortunate that we don't
know the access route. All the terrestrial mammal species that I
commented on, game animals and the wolverine and so forth, are
very affected by access corridors, and of all the access routes that
have been proposed, the ones that are most -- the one that would be
most serious is the Denali, the one up Deadman Creek and to the
Denali Highway. And that one is still under consideration.
And that -- you know, that would have serious impacts on
moose, caribou, Dall sheep, wolves, and bears, very serious impact,
much more so than any of the other corridors.
So I think trying to design impact assessment studies, absent
knowledge of where the access would be, is a flaw. And it's
unfortunate that that's the case. And I'm not sure why we don't know
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what the access route is, but really, the studies for the species of
interest should have prior knowledge of what that access is going to
be. [3:55:12]
And so that the -- because the impacts are going to depend on
that access, that just to say we collected data and once we know the
access, we'll be able to interpret that data correspondingly, is not
really correct. I think you have to know the access in order to
evaluate and design your studies appropriately.
The third comment is that -- is that one of the things that
commonly happens and almost always with impact assessment
studies is that you design a bunch of studies to evaluate how the
current habitat is being used by various species, and then you make
guesses about how those impacts, once they occur, will affect those
species. And that is what impact assessment is all about.
However, what is really, really needed and has been done way
too -- way too rarely, is to design post-project studies to evaluate the
accuracy of the guesses that were made in the pre-project studies.
And really, on a project of this magnitude, I think it would be
appropriate to -- to assure the concerned public that work will be
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done after the project is constructed. If it is constructed, that will
help us make better guesses about how the impacts will occur in the
future.
So I just want to -- I don't know how that would fit into the
design, but I think it's unfortunate that that is not a component of any
of the studies I saw.
Now, when we did this work in the '80s, of the stuff I had
done, we tried to design techniques in most cases so that those
impact studies would be done, even though that wasn't -- wasn't
really an objective and we didn't have any money for it, but we tried
to design the studies so that they could be -- you could generate -- if
you found money and time, generate evaluations of how valid or
invalid your predictions were.
My last and final comment is that I don't think that the studies
that I evaluated, which are the ungulates and the large carnivores and
the wolverine, really paid very much attention to the studies that
were done in the '80s. You know, there was some listing of it.
But really, what those studies did in the '80s were, you know,
they listed a bunch of impacts and that they suspected to be the case.
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And at some level -- and you know, I can't be very specific about this
unfortunately, but at some level I think it would have been better to
have seen more indications than we currently have, that the current
studies were built on those earlier studies, and designed to refine the
kind of estimates -- what we see instead are an objective in many of
these studies saying the historical studies will be taken into account
at some point for the final examination. That's what we see.
But in fact, the current study should have been designed based
on what these historical studies were and their -- and their findings,
and that would have, I think, made a stronger set of studies.
And once again, thank you very much for the opportunity to
make these comments.
MS. MCGREGOR: Well, we appreciate the input. I can
address a few of those -- the second point that you made about the
access route.
There is a reason that we have several alternatives to consider.
That's part of going through the NEPA process, and also for our 404
permit, trying to figure out which would be the least environmentally
damaging alternative.
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So the studies are designed to study all of those corridors so
that we can do a complete alternatives analysis. So that's why one
hasn't been decided on. The location of the corridor itself is a big
enough project compared to -- I mean, actually constructing a dam
and putting it on the river. It is a significant issue. We recognize it's
a significant issue, and that's why we have a complete set of studies,
so we can do the comprehensive alternative analysis.
With respect to the studies being designed based on current
information and the need for post-project studies, the studies were
designed so that we could collect baseline data to be able to conduct
project impact assessments as well as development of protection
mitigation and enhancement measures.
As part of FERC's license and the settlement agreement, there
will be mitigation for project effects, and their monitoring will be
part of assessing the project impacts moving forward. So that is a
component of this process. It's just not part of the phase that we're at.
MR. MILLER: And the difference between monitoring
mitigation and monitoring impacts, and that's -- and so I -- there's a
distinction there.
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MS. MCGREGOR: Understood. And with respect to the
current studies including the 1980s information, they did. We
actually used the impacts -- the impacts that were identified for each
resource area, we went from the 1980s, we went through that. All of
our contractors have reviewed the 1980s information, whether or not
that's been completely used in the comprehensive analysis, that's
been put out in a document is -- you know, that hasn't occurred yet
for some resource areas, some more so than others.
But that was the basis of designing a study. So that was the
first step was for people to look at the historical information as well
as the existing information, and then build upon that moving
forward, again, with the whole premise of what kind of baseline data
do we need to collect to be able to do a project impact assessment
and then develop [4:01:23][appropriate studies] moving down the
road.
So, and I recognize that you're new to the -- to our process that
we've had underway through the last three years.
I just want to add a few wrap-up comments. I appreciate very
much the people that were prepared for this meeting. It allowed us to
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have a useful conversation, I think, for both our contractors here
conducting the studies for AEA as well as other licensing
participants. It's what this process is supposed to be like, especially
at this stage, so we appreciate that feedback and those comments.
We are going to go through the comments we received. We'll
try to determine whether or not there's a need to provide additional
information in this process. AEA's not obligated to provide any
additional information before the USR, but we are also trying to have
an open process and make data available, QA/QC’d data publicly
available as it becomes available to us. So we'll look through the
comments we've received today from various participants and see
when certain information will be available, and then we'll provide
that.
That's all I have.
MR. GILBERT: Anybody on the phone have any follow-on
questions, thoughts?
MR. KONIGSBERG: Well, yeah, Kirby.
MR. GILBERT: Jan?
MR. KONIGSBERG: Can you hear me?
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MR. GILBERT: Yeah, sure.
MR. KONIGSBERG: Jan Konigsberg.
MR. GILBERT: Sure.
MR. KONIGSBERG: Yeah, Jan Konigsberg. I have -- I
guess I will just express my disappointment in not hearing from
FERC contractors with respect to the review they had done so -- of
the ISR. A number of [4:03:20][letter was] filed, as most of you
know, a letter requesting that sort of participation prior to these
meetings, and I was hoping that we would get the benefit of that
review that has been conducted, in terms of FERC's study plan by
their contractors, at least through FERC's permit
[4:03:46](indiscernible) not just the contractors.
And I think it would have, you know, helped in terms of
discussion thus far, and at least getting some sense of where the
differences or agreements lie with respect to the data gathering and
information synthesis, and I’m only -- I'm expressing it from a
standpoint as the lead federal agency on this, and with respect to
its -- its ultimate responsibility with the public trust resources that are
involved in this project, and we, the public, that have been involved.
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And a number of us, who don't have the expertise to
understand all the -- to delve into these studies to the extent it's
required, would have benefited from the work that's already been
done, in the same way that AEA's contractors have brought their
work to us, as well as from the agency and their contractor.
It's just a statement. I don't necessarily require a response,
unless FERC would like to respond at this point about that particular
lack of participation. But again, you know, it is discouraging from
that, in terms of that aspect of the proceedings so far, at least for me.
MR. GILBERT: Okay. Good observation.
Anybody else on the phone?
MS. WOLFF: Yeah, Kirby, this is Whitney.
There may not be anybody who I can ask this, but I had a
battery issue during the habitat mapping, and I'm wondering if there's
anybody there to answer a quick question, if you can direct me to
where I should send it.
MR. GILBERT: Well, if it's -- go ahead and ask it.
MR. SCHICK: Go ahead.
MS. WOLFF: Okay. It's just for 10.19, the habitat use study.
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And I went through all three Parts, A, B, and C, and I see in the Part
C has added Denali East, but it's not clear to me if you pulled the
Chulitna Corridor out. And if you did, I don't understand where the
north and the west boundary above Gold Creek is on that study area.
MR. SCHICK: The Chulitna Corridor --
MS. WOLFF: If somebody can --
MR. SCHICK: This is Terry Schick with ABR.
MS. WOLFF: Okay.
MR. SCHICK: In the ISR, the study area maps that you see
represent what would have been done in 2013 had we done anything
with that study in 2013.
MS. WOLFF: Yeah, right. I understand that. And I read Part
C, where you had the differences. And I see you added Denali East,
but it doesn't say that you pulled Chulitna.
MR. SCHICK: Yeah.
MS. MCGREGOR: It should be in the slide.
MR. SCHICK: Assuming that the Chulitna Corridor is
definitely removed, that would be removed from the 10.19
Evaluation of Wildlife Habitat Use study.
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MS. WOLFF: Okay. So then where does that -- so that just
puts the northwest boundary two miles off for now, not four, north of
the Susitna; is that correct?
MR. SCHICK: Yes. Yeah. This study, 10.19, mirrors exactly
the study area boundaries in the wildlife habitat and
vegetation mapping study.
MS. WOLFF: Right. 11.5 and 11.6. I've got all that. I
just -- it's an open-ended boundary there, even on your original map.
It doesn't really show where that northwest corner is. And now that
you've changed it quite a bit, I just want to make sure I understand it.
MR. SCHICK: Yes. The Chulitna Corridor, assuming it is
officially dropped, will be removed from that study area.
MS. WOLFF: Okay. And then the last quick question I have
on that is that in the study objectives, it talked about species of
concern, and but later lists that it's going to include all the data from
10.5 to 10.18. So I just want to make sure that species of concern
takes in all of the studies we've discussed today and isn't -- it isn't a
finer subset of species.
MR. SCHICK: Yes. For 10.19, one of the modifications is
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that we will assess habitat values for all bird species that have been
recorded in the area, so that's going to, by definition, include all of
the bird species of conservation concern.
And then for mammals, there will be a selection of species,
and one of the big selection criteria will be species of management
and conservation concern. So those --
MS. WOLFF: Okay. And do we know what those species are
yet?
MR. SCHICK: We don't. We haven't done that selection of
species yet.
MS. WOLFF: Okay. I'd just like to hope that we see
some -- some moose habitat covered in that. You know, the moose
study primarily just up there at the project site really is limited to that
upper river area, and it would be nice to see the effect of the moose
habitat down in the middle lower river.
MR. LAWHEAD: Yeah. Moose will definitely be one of the
species.
MR. SCHICK: Yeah. We can guarantee that moose will be in
there.
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MS. WOLFF: Good.
MR. SCHICK: Management species -- mammal management
species will most certainly be selected. That's like criterion number
one for selection of mammal species for analysis.
MS. WOLFF: Okay. And then maybe we'll see that list at
some point? Do you know when that might be?
MR. SCHICK: We don't know when that might be, actually.
The study's been deferred to 2015, so it would be conducted after
wildlife survey studies are completed and after the habitat mapping
in 11.5 and 11.6 has been completed. So the answer is we don't
know when that species list would be available for review at this
time.
MS. WOLFF: Okay.
MS. MCGREGOR: We will --
MS. WOLFF: Okay. I really appreciate you taking my
questions after, and I apologize for jumping in at the very end here.
Thank you.
MR. GILBERT: That's okay.
MS. MCGREGOR: No. That's fine, Whitney.
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And just to let you know, I mean, right now things will be up
in the air, but -- with FERC study plan determination or fiscal cycle -
- but when we sort out what we are going to do in 2015, we will start
the technical work group meetings up again, and those will be
providing updates for each of the studies.
MR. GILBERT: Yes.
MS. WOLFF: All right. Thanks so much.
MR. WINCHELL: Yeah, this is Fred Winchell, FERC
contractor. And I need to respond to the previous comment, that we
are listening in on this primarily to understand where the concerns
are and what types of study modification requests we may have to
deal with in the determination. So we don't want to take up time in
these calls and meetings. We want the stakeholders to have their
chance to say their state -- state their positions, so we can be ready
for what is going to come in in your formal comments on this
proceeding.
And so we have held back a little bit on stating our position,
but we are listening and chiming in when we think it's helpful. That's
all I have to say.
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MS. MCGREGOR: Thank you.
MR. GILBERT: Thanks.
UNIDENTIFIED MALE: Who was that?
MR. GILBERT: It was a contractor to FERC.
MS. MCGREGOR: Fred Winchell.
MR. GILBERT: Yeah. I thought I said Fred. Okay.
Anything else?
MR. WINCHELL: Sorry I'm a little grumpy, but I'm
recovering from jet lag from coming back from Anchorage.
MR. GILBERT: Oh, okay. Because you were here last week.
MS. MCGREGOR: And it's 8:00. Are you on the East Coast?
MR. GILBERT: Yeah. You're, like, Boston, aren't you?
MR. WINCHELL: Yeah.
MR. GILBERT: Yeah. Okay.
MR. WINCHELL: It's a long way.
MR. GILBERT: Okay. Good.
Well, if there's nothing left, we'll close this one out.
MS. MCGREGOR: We can adjourn. That's a lot of material
we covered today.
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MR. GILBERT: Yeah. Thanks. Thank you, everybody, for
participation and appreciate. A lot of good information.
And we'll start tomorrow on the physical sciences for anybody
interested.
UNIDENTIFIED FEMALE: And it starts at 8:30, correct?
Nothing has changed?
MR. GILBERT: Yeah.
MS. MCGREGOR: 8:30.
MR. GILBERT: The agenda, we're going to try to stick to it,
and that's the way we're going to go, yeah.
UNIDENTIFIED FEMALE: Thank you, guys.
MR. GILBERT: Thanks, everybody on the line. Bye bye.
4:12:58
(Off record.)
SESSION RECESSED
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