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Susitna-Watana Hydroelectric Project Document
ARLIS Uniform Cover Page
Title:
SuWa 256
Initial Study Report Meetings, October 16, 2014 : Millennium Hotel, 4800
Spenard Road, Anchorage, Alaska 99517
Author(s) – Personal:
Author(s) – Corporate:
Initial Study Report Meetings (2014 October 16 : Anchorage, Alaska)
Of the seven presentations, five had been prepared by Tetra Tech, Inc.
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 256
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 B
Document type: Pagination:
Technical memorandum 405 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 (SuWa 255) and C-N (SuWa 257-268)
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.
Pages 100-115 in Part B have been replaced by updated pages. Those replacement pages
originally appeared on pages 19-34 of SuWa 268, which is Attachment N.
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 16, 2014
Part A – Transcripts
Millennium Hotel
4800 Spenard Road
Anchorage, Alaska 99517
Filed November 15, 2014
SUSITNA-WATANA HYDRO
Agenda and Schedule
Initial Study Report (ISR) Meetings
Glacial and Groundwater (Studies 7.5 and 7.7)
Geomorphology (Studies 6.5 and 6.6)
Water Quality (Studies 5.5 - 5.7)
Millennium Hotel
4800 Spenard Road
Anchorage, Alaska
October 16, 2014
_______________________________________________________
ATTENDEES
Emily Anderson, Wild Salmon Center
Julie Anderson, Alaska Energy Authority
Nate Anderson, Alaska Energy Authority
William Ashton, DEC
Greg Auble, U.S. Geological Survey
Jessica Blizard, Tetra Tech
Martin Bozeman, Alaska Energy Authority
Phil Brna, U.S. Fish and Wildlife Service
Bryan Carey, Alaska Energy Authority
John Clark, St. Hubert Research Group
Jason Conder, Environ International
Justin Crowther, Alaska Energy Authority
Matt Cutlip, Federal Energy Regulatory Commission
Connie Downing, Tyonek
Paul Dworian, URS
Wayne Dyok, Alaska Energy Authority
Kevin Fetherston, R2 Resource Consultants
Bill Fullerton, Tetra Tech
Sara Fisher-Goad, Alaska Energy Authority
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
Hal Geiger, St. Hubert Research Group
Harry Gibbons, Tetra Tech
George Gilmour, Meridian Environmental
Dara Glass, CIRI
Domoni Glass, Environ International
Leanne Hanson, U.S. Geological Survey
John Hamrick, unidentified (phone)
Mike Harvey, Tetra Tech
Stormy Haught, U.S. Fish and Game
Jeremy Hayes, MSI Communication
Sandie Hayes, Alaska Energy Authority
Phil Hilgert, R2 Resource Consultants
Graham Hill, Northwest Hydraulic Consultants
Chris Holmquist Johnson, U.S. Geological Survey
Nick Jayjack, Federal Energy Regulatory Commission
Andy Josephson, Alaska Legislature
MaryLouise Keefe, R2 Resource Consultants
Joe Klein, Alaska Department of Fish and Game
Jan Konigsberg, Alaska Hydro Project (phone)
Felix Kristanovich, Environ International
Ellen Lance, U.S. Fish and Wildlife Service
Michael Lilly, GWS
Becky Long, Susitna River Coalition
Betsy McCracken, U.S. Fish and Wildlife Service
Betsy McGregor, Alaska Energy Authority
David McLean, Northwest Hydraulic Consultants
Jim Munter, J.A. Munter Consulting
Sarah O'Neil, Trout Unlimited
Doug Ott, Alaska Energy Authority
Becky Nichols, Analytica Group
Laura Noland, Environ International
Doug Ott, Alaska Energy Authority
Steve Padula, McMillen
Kathryn Peltier, McMillen
Guy Phillips, Kier Associates
Dudley Reiser, R2 Resource Consultants
Elizabeth Rensch, Analytica Group
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
Greg Reub, Environ International
Tyler Rychener, Berger/FERC
Hal Shepherd, Fish & Water Advocacy (phone)
Corinne Smith, Nature Conservancy
Marie Steele, Alaska Department of Natural Resources
Miranda Studstill, Accu-Type Depositions
Wayne Swaney, Stillwater Sciences
Cassie Thomas, National Park Service
Rachel Thompson, Alaska Energy Authority
Unidentified Female (phone)
Unidentified Male (phone)
Unidentified Male (phone)
Unidentified Male (phone)
Unidentified Male (phone)
Unidentified Male (phone)
Unidentified Male (phone)
Gary Van Der Vinne, Northwest Hydraulic Consultants
Jose Vasquez, Northwest Hydraulic Consultants
Lori Verbrugge, U.S. Fish and Wildlife Service
Sue Walker, National Marine Fisheries Service
Aaron Wells, ABR
Fred Winchell, Louis Berger
Gabriel Wolken, Alaska Division of Geological Surveys
Mike Wood, Susitna River Coalition
Ed Zapel, Northwest Hydraulic Consultants
Lyle Zevenbergen, Tetra Tech
Jon Zufelt, HDR
INTRODUCTION
MR. PADULA: Hello again, everyone that was here
yesterday. And I see some new faces in the crowd. I’m Steve
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
McMillan. My role today is for me to be the facilitator and hopefully
make this an effective meeting for everyone, for us to share
information.
A few housekeeping items. In case of an emergency, any of
these exits will get you out to the main hallway, and there's a set of
stairs that will get you downstairs. Restrooms, straight out and to the
right, down at the end of the hall.
We will have folks on the phone, as yesterday, again we hope
that we've solved some of our sound issues. But again, if you're
going to speak today in the room, you definitely need to use one of
the microphones. And even with a microphone, you have to be very
directly talking into it. This is your chance to be a rockstar, so
embrace it. If you turn your head at all, we cannot pick up the sound
in the microphone and we'll try to remind folks of that.
There will be breaks, a lunch break like yesterday. There will
be an opportunity to caucus, if folks need that time. We would
appreciate mostly doing that around breaks for lunch, but if need be,
just let us know and we'll accommodate that.
Miranda is our court reporter again. So again, identify
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
yourself, if you would. If not, I'll probably identify you, but it
would be great if you could state your name when you're making
your comments.
And try not to talk over one another. Again, that makes it a
little challenging for the court reporter.
With that, again, this is day two of three days of meetings this
week, on what we call the wet studies related to the Susitna
licensing. There's three more meetings next week. Again, welcome
back to the folks who were here yesterday. Let's start with a quick
set of introductions around the room. Just yell, Bill.
MR. FULLERTON: I'm Bill Fullerton with Tetra Tech and
I'm the lead for the geomorphology studies.
MR. HARVEY: Mike Harvey, Tetra Tech, geomorphologist.
MR. ZEVENBERGEN: Lyle Zevenbergen, Tetra Tech,
geomorphology modeling
MR. WOLKEN: Gabriel Wolken with the Alaska Division of
Geological & Geophysical Surveys. I’m the lead for the Glacier
Runoff study.
MR. DYOK: Good morning, Wayne Dyok, Alaska Energy
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
Authority.
MS. MCGREGOR: Alaska Energy Authority.
MR. LOVE: Matt Love, Van Ness Feldman.
MS. GLASS: Dara Glass, CIRI.
MS. LANCE: Ellen Lance, Fish & Wildlife Service.
MS. McCRACKEN: Betsy McCracken, Fish and Wildlife
Service.
MS. WALKER: Sue Walker, National Marine Fisheries
Service.
MR. JAYJACK: Nick Jayjack, FERC.
MR. CUTLIP: Matt Cutlip, FERC.
MR. KLEIN: Joe Klein, Department of Fish & Game.
MR. CROWTHER: Justin Crowther, AEA.
MS. PELTIER: Kathryn Peltier, McMillen.
UNIDENTIFIED MALE: (Indiscernible - distance from
microphone.)
MR. RYCHENER: Tyler Rychener, Louis Berger, contract
team.
MR. WINCHELL: Fred Winchell, Louis Berger, FERC
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
contract team.
MS. THOMPSON: Rachel Thompson, Alaska Energy
Authority.
MR. OTT: Doug Ott, Alaska Energy Authority.
MR. KRISTANOVICH: Felix Kristanovich, Environ
International.
MR. CONDER: Jason Conder, Environ International.
MS. GLASS: Domoni Glass, Environ.
MR. REUB: Greg Reub, Environ.
MR. HOLMQUIST-JOHNSON: Chris Holmquist-Johnson,
USGS.
MS. HANSON: Leanne Hanson, U.S. Geological Survey.
MR. BOZEMAN: Martin Bozeman, AEA.
MR. ANDERSON: Nate Anderson, Alaska Energy group.
MS. ANDERSON: Julie Anderson, Alaska Energy Authority.
MR. CAREY: Bryan Carey, AEA.
MR. MUNTER: Jim Munter, J.A. Munter Consulting,
contractor for National Marine Fisheries Service.
MR. REISER: Dudley Reiser, R2 Resource Consultants.
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
MR. HILGERT: Phil Hilgert, R2 Resource.
MR. BRNA: Phil Brna, Fish and Wildlife Service.
MR. HILL: Graham Hill, Northwest Hydraulic Consultants.
MR. GILMOUR: George Gilmour, Meridian Environmental,
on behalf of the agencies.
UNIDENTIFIED MALE: (Indiscernible - distance from
microphone.)
MR. PHILLIPS: Guy Phillips, Kier Associates.
MR. FETHERSTON: Kevin Fetherston with RZ.
UNIDENTIFIED MALE: (Indiscernible - distance from
microphone.)
UNIDENTIFIED MALE: (Indiscernible - distance from
microphone.)
MR. MCLEAN: David McLean, Northwest Hydraulic
Consultants.
MS. LONG: Becky Long, Susitna River Coalition.
MS. THOMAS: Cassie Thomas, National Park Service.
MR. WOOD: I'm Mike Wood, Susitna River Coalition.
MR. CLARK: John Clark, St. Hubert Research Group.
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
UNIDENTIFIED MALE: (Indiscernible - distance from
microphone.)
MR. AUBLE: Greg Auble, USGS.
MR. DWORIAN: Paul Dworian, URS.
MS. BLIZARD: Jessica Blizard, Tetra Tech.
MR. GIBBONS: Harry Gibbons, Tetra Tech.
MS. KEEFE: MaryLouise Keefe, R2 Resource Consultants.
MR. LILLY: Michael Lilly with GW Scientific.
UNIDENTIFIED MALE: (Indiscernible - distance from
microphone.)
MR. PADULA: And obviously it would have been hard to
pass the mic around -- oh, I'm sorry, someone else?
So again, folks in the room, please, if you haven't, please sign
in so the transcriber can go get that list and be able to match names to
people.
So now, for folks on the phone, please introduce yourselves.
UNIDENTIFIED FEMALE: Jessica
(Indiscernible - interference with speaker-phone.) Alaska Operations
office.
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
UNIDENTIFIED MALE: (Indiscernible - interference with
speaker-phone.) Tetra Tech.
UNIDENTIFIED MALE: (Indiscernible - interference with
speaker-phone.) Northwest Hydraulic Consultants, advising Services
on (indiscernible).
UNIDENTIFIED MALE: (Indiscernible - interference with
speaker-phone.)
UNIDENTIFIED MALE: (Indiscernible - interference with
speaker-phone.)
MR. KONIGSBERG: Jan Konigsberg, Alaska Hydro Project.
UNIDENTIFIED MALE: (Indiscernible - interference with
speaker-phone.)
MR. SHEPHERD: Hal Shepherd, Fish & Water Advocacy
UNIDENTIFIED MALE: (Indiscernible - interference with
speaker-phone.) with FERC.
UNIDENTIFIED MALE: (Indiscernible - interference with
speaker-phone.) Stillwater Sciences, contractor to FERC.
MR. PADULA: Okay. Thank you. And again, I'd like to
remind you folks on the phone, if you have comments or questions,
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
you really need to speak up.
So just a couple of introductory slides, and then Wayne will
have a couple of remarks to make.
MR. DYOK: I'm going to pass today, I think there's almost
the same group here that was here yesterday.
MR. PADULA: Okay, great. It will gain us back some time.
So just the first slide here, summarizing the purpose of the
meetings this week and next week, this is really a check-in progress
meeting on the work done and reported on so far in the Initial Study
Report, opportunity for discussion about study results.
And also, again, any modifications or variances that might
have occurred during the conduct of the study so far, as well as any
proposed modifications by AEA for the upcoming work, and then
there's obviously the opportunity for others to weigh in on any
modifications that they may think are appropriate for the studies.
Those of you who have been in the process for a while will
recall that actually last February, there was a draft ISR put out and,
then the final official ISR was filed with FERC in June.
Because of the amount of information, FERC extended the
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Susitna-Watana Hydro ISR Meeting
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review time through October 1st, which leads up to these sets of
meetings.
Then there were a series of supplemental technical
memorandums that were issued last month. And again,
given -- given that additional information, there's been additional
time granted for the review of that information, and that will lead to a
subsequent set of meetings in January that will be specifically
focused on covering the information that's reported in those technical
memos.
Basic schedule here, this matches up with the information that
was in FERC's last guidance letter. So again, the meetings this week
and the meetings in January will be captured in meeting summaries
which will be issued by January 22nd.
There's a 30-day period for licensing participants to file
comments on the meeting summaries, as well as their
recommendations for either modifications to existing studies, or if
they think there is a need to initiate a new study.
Then a 30-day period for response to those comments, and
then 30 days later FERC will issue its determination as to the specific
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Susitna-Watana Hydro ISR Meeting
October 16, 2014
requirements for modifying the study plans before additional work
continues in the next year.
And then the last two are the placeholder dates for issuance of
the updated study report and another set of meetings similar to these
meetings.
Again, this information has been out there on the Web for a
while, so I'm not going to go into this in detail. This just summarizes
the topics that are covered three days this week and the three days
next week.
Again, the basic structure of the Initial Study Report, you'll
remember again, the part A is what was in the draft ISRs, and we
committed not to change that. So when the finalize ISRs went out in
June, that became part A. Part B was errata, any supplemental
information, so folks could find that more easily, and then part C was
any new material that had not been included in the draft.
The approach for today, as yesterday, is really to encourage
discussion. I thought we did a really good job collectively of that
yesterday, so we are again going to keep our presenters as close to
ten minutes as we can.
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Susitna-Watana Hydro ISR Meeting
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We've got fewer studies to do today, so we may give some of
our presenters a little leniency. But still, we're going to try to get
through the presentations rather quickly and focus in again on
variances, quick summaries of results that've already been available
to you folks, and then proposed modifications. And so that will
hopefully trigger, again, the same kind of effective conversations we
had yesterday.
And the last three slides, which I will not show, are basically
FERC's regulatory requirements for requesting modifications to
study plans or requesting a new study. Those are on the Web. They
are also up on the wall on both sides of the back of the room, if you
are interested.
And with that, Wayne, nothing? Anybody else have any
comments? Microphone, please.
MS. LANCE: I just wanted to acknowledge the change in
format yesterday really -- the participants really appreciated it and it
facilitated some good conversation of the 2013 (indiscernible), so
thank you.
MR. PADULA: Okay. Do you want to start out, Gabe?
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Susitna-Watana Hydro ISR Meeting
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GLACIER AND RUNOFF CHANGES (STUDY 7.7)
MR. WOLKEN: Okay, and I understand that based on the
format yesterday, there's more interesting discussion than on the
content in the presentations, so I'll summarize this as quick as
possible so we can move on to discussion.
The objectives of this study, the ISR portion of this study, was
really to review the existing literature and data that's relevant to the
glacier retreat in South Central Alaska and the Upper Susitna
watershed.
And this really includes an evaluation of all the relevant data
regarding glacier melts and runoff in the Upper Susitna Basin, that is,
above the dam. And the review summarizes the current
understanding.
And so with that, there are multiple components to this study.
Looking at the -- effectively the cryosphere, the snow and ice
components within the Upper Susitna Basin.
There are no variances to this study.
And I'll just summarize some of the salient points quickly.
It's instructive to go to a broader context to understand what's
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Susitna-Watana Hydro ISR Meeting
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actually happening in the Upper Susitna Basin, given the lack of data
that actually exists for this region.
So this slide is to help illustrate a global perspective on mass
budgets in specific geographic regions throughout the globe. And
the red circles there that you see are an indication of the mass
budgets. The red indicates that it's a negative mass budget of glaciers
in these different regions.
I'll just draw your attention to the northern hemisphere, you
see that there's a lot of red there, a lot of red dots. And in particular,
I probably should mention, in Alaska, which does show one of the
largest dots in the northern hemisphere, and that does illustrate that
Alaska is one of the places where we do see the greatest mass loss in
glaciers in the United States.
The large circle does indicate the area. That's instructive to
look at as well, as it gives some sort of analogue to the amount of
melt that can occur there, though it does ignore volume.
Now, this is direct linkage to warming climate, global
warming of the climate, and it's specifically related to, as this slide
shows, the (indiscernible) trend.
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Susitna-Watana Hydro ISR Meeting
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Looking at anomalies here from the 1951 to 1980 period, you
do see that the red indicates temperature anomalies. Blues indicate
negative anomalies. The northern hemisphere clearly has strong lean
toward the positive anomaly sides, up to 2.5 degrees over the last
decade.
This extends to Alaska, as well. And so while the datum is
slightly different here, the trend is the same. And so within the
period 1949 to 2011, we do see that we have increases in
temperatures, positive temperature, surface air temperature
anomalies.
And within the study area, around 2.5-degree increase from
1949 to 2011.
This very busy slide is here just to alert you to the fact that
there are a lot of studies in Alaska using a variety of different
methods to look at mass loss, none of which focus specifically on the
Upper Susitna Basin.
These studies do show that there has been a trend, from -
- starting around 1955 up to the present of negative mass loss. And
so that highlighted column there, you'll see lots of negatives there.
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Susitna-Watana Hydro ISR Meeting
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There's a trend, and that's what we're looking at. We anticipate this
trend to continue.
And this is some work by Regine Hoff and Valentina Aradic
showing the volume reduction, as modeled with 14 different climate
model scenarios. The projection here out to 2100 of glacier volume
loss is evident.
In a shorter time span, the glacier mass loss is a positive
feedback effect, effectively, showing that as you reduce mass in the
glacier, there's a firn reduction in the snow reduction. This causes
more bare ice to be exposed, which actually causes a lower albedo,
which means we actually have a little bit more mass loss every year.
This also means that there's going to be lower water retention
in the specific reservoirs of snow and firn, meaning that we can't hold
as much water, so we're going to have a faster through-flow of water
and large peak flows.
Long-term perspective, there's -- as climate warms, mass loss
increases and as that mass loss increases, then the volume of the
glaciers decrease.
Now, the key question here is as that volume decreases, on the
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runoff curve that you see on the bottom there, what happens and
where are we sitting?
And in this case, with the Upper Susitna Basin, we really don't
know at this point, based on the literature review, whether or not
flows will increase or will decrease at this point.
This is just an illustration of the data that's available within
120 kilometers of the Upper Susitna Basin, the red delineated basin
there, and the dots indicate the different climate stations that are
available to help provide some indication of what might be
happening in this area.
And as you can see within that basin and highlighted here,
there are only a few stations -- climate stations that are actually
within the Upper Basin that provide some direct information about
the climate variables.
And as you can see also by this, there is a -- basically a
fragmented record within these records.
Also available through this ISR study is a wealth of knowledge
from the previous work that was done in the 1980s. And from that,
we were able to recover meteorological stations, records from the
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stream gauges that were installed, and as well as mass balance
records directly from five glaciers. I don't know how many glaciers
exist in the Upper Susitna Basin.
We were also able to recover snow depths, which were very
informative to help get an idea of what the snow distribution is.
These are -- granted, these are point snow-depth measurements, but
these also come from the 1980s.
And finally, here's an illustration of the amount of knowledge
that we have on effectively the state of the cryosphere within the
Upper Susitna Basin. And this shows the distribution of permafrost
and glaciers. Again, there's over a hundred glaciers within the Upper
Susitna Basin. It's comprised principally of continuous and
discontinuous permafrost regions and some sporadic areas, mostly
constrained to the rivers.
We do have some data associated with permafrost ground
temperatures and permafrost depths, and we also have some modeled
variables that we can draw from within the published literature of
mean annual ground temperature profiles.
This is the required portion of the study, and it’s considered
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complete.
And with that, I guess I will open it up to questions.
MR. WANEER: (Indiscernible - over-modulating.)
MR. PADULA: Could you please speak up a little bit?
MR. WANEER: Can you hear me?
MR. PADULA: Yes.
MR. WANEER: Yes? Okay. One of the
(Indiscernible - over-modulating.) I did not see that included in the
initial report. (Indiscernible).
MS. WALKER: I can understand.
MR. WANEER: (Indiscernible - over-modulating
MR. WOLKEN: I didn't quite catch that, but is the question
about sediment production?
MR. WANEER: (Indiscernible - over-modulating)
MS. WALKER: This is --
MR. WANEER: (Indiscernible - over-modulating)
MS. WALKER: Do you know who it is? Do you know who it
is?
MR. WANEER: (Indiscernible - over-modulating.)
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MS. WALKER: I know what he's asking, because I was going
to ask the same thing. Do you want to ask him to clarify?
It was very hard to hear Waneer. This is Sue Walker with
NMFS. But I believe your first question is the same question that I
had, and that is if the FERC-ordered study plan did require an
assessment of the effects of surging glacier on sediment deposition in
the reservoir. Particularly there was a unpublished 2012 report. And
I had asked about that report and been told it's within the
geomorphology, but I have searched and searched and I can't locate
it.
And I don't think we could understand the other -- I believe
you had two more points to your question, Waneer?
MR. WANEER: Yeah. I had (indiscernible - over-
modulating) geomorphology study or not – I didn’t see any mention
of that in this report.
MR. DYOK: You might want to come up to the table mic.
MR. PADULA: It would be helpful, yes. So I think the
question had to do with the potential for increased sedimentation in
the reservoir due to glacial surge.
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And were there other components to the question?
MR. WANEER: No, no. that's it. (Indiscernible - over-
modulating).
MR. FULLERTON: Okay. And we did some investigation of
the issue of the glacial surge.
We contacted Harrison, yes, Dr. Harrison from University of
Alaska Fairbanks, had a discussion with him concerning his -- the
glacial surge.
And also one of the things that we did just this last field
season, was do a reconnaissance of the upper river, starting at the
Cantwell Bridge, on downstream, were able to observe a lot of the
sediment supply that's been coming off the glaciers and getting into
the river and Mike here he did that reconnaissance and has been
looking at the issue of the glacial surge, so Mike has.
MR. WANEER: Right. (Indiscernible - over-modulating.)
MR. FULLERTON: Well, if you want to -- first, Mike,
characterize our conversation we had with Dr. Harrison.
MR. JAYJACK: I think what he's asking is where is it in the
ISR.
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MR. FULLERTON: We -- we don't have it -- it isn't in the
ISR. We haven't put that information in there at this point.
MR. HARVEY: Maybe I can just expand on that a little bit.
This issue of the glacial surge was brought up in a public
meeting by Dr. Harrison at one of the meetings.
We contacted him. There were data, but the last time when the
glaciers surged was 1985, towards the end of the last Susitna project.
He and some others had collected some data on sediment, but
we and -- neither he nor we have been able to get our hands on that
information. It was never formally put into a report and he thinks it's
probably in the notebooks and stuff of colleagues scattered in many
places, many of whom have retired at this point.
However, the point I would make is that in our discussions
with him, he actually just said -- it was sort of more of a throw-away
comment, he actually believes that -- at least this is what he told us,
that the -- with increased global temperatures, the probability of
surging on the Susitna glaciers is likely to be less than it has been
historically. Now, I'm not a glaciologist, I just repeat what he said.
That's point 1.
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Point 2 is that even the data they did collect, there is so much
distance between the Cantwell -- where the Cantwell gauge was,
where they collected some data, and the glaciers, you've got a vast
storage of sediment in that area. The river's transporting at capacity.
Now, you can't transport more sediment than at capacity.
And based on our field work this year, that whole upper river
is pretty much sand. There's almost no gravel in that upper part of
the river. It's sand.
The USGS has a publication -- an individual from the USGS,
has a publication back in the '80s, that actually looks at the
partitioning of sediment from the glaciers and the distance
downstream, and the conclusion in that paper certainly supports what
we saw out there. That the gravel does not get out, the gravel stays
up, it's the sand that comes through, and that's the [primary sediment
supply] from the upper river on the glacier side for at least the river
dynamics and a portion of this is the important fraction, this sand, not
the gravel.
And believe me, I can guarantee you, there's a hell of a lot of
sand there. We more or less had to carry our boats through sections
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tryi ng to find water just to, you know, get them through. So it's sand
and almost an infinite quantity of sand in place in storage up there.
So I don't think surges or anything else are going to, in fact,
increase the amount of sand that can be transported out of the upper
river.
MR. WANEER: I have a question. In your slides, can you go
back to number 7? Slide number 7?
MR. WOLKEN: Now, can you repeat that, please?
MR. WANEER: (Indiscernible - over-modulating.) have you
seen any such (indiscernible - over-modulating) run-off or
(indiscernible - over modulating)?
MR. WOLKEN: I think you said are there any trends in
precipitation and runoff, and if that is the question, then yes, we
did --
MR. WANEER: Yes.
MR. WOLKEN: -- we did uncover the available data and we
did look at that.
There are so few precipitation measurements and so few
reliable precipitation measurements within the study area or within
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the proximity of the study area, but no real trends could actually be
established.
MR. PADULA: Any additional questions?
MS. WALKER: Hi, this is Sue Walker with NMFS.
We've had some conversations with AEA with Wayne Dyok
and with Bryan Carey, Gabe, about your report, and they indicate
that your report will be available around the first of the year. Is that
on schedule?
MR. WOLKEN: We've got an initial draft that will be
available in February.
MS. WALKER: February?
MR. WOLKEN: Yes.
MS. WALKER: When in February?
MR. WOLKEN: I think we have the end of February is the
target date for that.
MS. WALKER: That's problematic for license participants.
We were -- we were informed earlier that it would be around the first
of the year. That's information we could use in making our requests
for modifications to studies, which we do intend to do.
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Based on the FERC director's determination, it was stated that
if there was additional information on the effects of climate change,
that it might be time now to make a request for a climate study,
which is really what this is. It's worded a little vaguely.
Is there any chance that we would be able to get your report in
time for us to make our request for changes to studies, which are due
to FERC by February 23rd?
MR. WOLKEN: Yes, I think in terms of the timeline, that
probably can't be changed too much, just based on what's left to do.
I'm happy to share anything that we have with you prior to the actual
publishing of that material.
MS. WALKER: Well, in lieu of that, I'm wondering if it
might be possible for the climate change technical work group,
which only met a couple of times, to get together and at least make
use of your study and your data, which is significant, which is the
best information we have.
MR. WOLKEN: Yes, I'm happy to do that.
MS. WALKER: Okay. Is that something that AEA would
agree to?
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MR. DYOK: Yes. This is Wayne Dyok with Alaska Energy
Authority.
Yes, Sue as we talked previously, certainly this is an important
study for us. We're doing it ourselves and not through the FERC
process, and when Gabe gets his work to a point where it makes
sense to discuss it, we're certainly happy to discuss that with you.
When we had talked earlier, we had talked about sometime in the
first part of 2015, and that's still our goal.
But we have to give Gabe, you know, the time to get his work,
you know, done, and when he gets to a point where he feels it's
appropriate to share results, we're happy to do that.
MS. WALKER: Thanks, Wayne. That doesn't really answer
the question, though. I asked if it might be possible for us to have a
meeting with your scientists so that we can have this information in
time for us to formulate our request for a change to the study plan?
MR. DYOK: Sue, as I said, were -- we would be happy to
meet with you and when we spoke on the phone, I asked Bryan
Carey to work with Gabe and you to look at a timetable that would
make sense to have a productive meeting, and I stand by that.
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MS. WALKER: I understand that, but the date that we were
given was around the first of the year. Late February is after the
timeline for the deadline for our requests for changes to studies. We
would have to make our study request without that information ,
without the best available information.
Is there any possibility that FERC would entertain a later date
for that study request that we could have this very site-specific
information?
MR. JAYJACK: This is Nick Jayjack from FERC.
The chances of extending the dates are going to be
pretty -- pretty low.
I'm not quite understanding the information you're looking for.
Is it information that was required as part of our study determination,
or is this the information that we didn't require but we said that AEA
could, nevertheless, if they wanted to, conduct it on their own?
MS. WALKER: It's both of those. It's both of those things.
It's the information that doesn't appear to be in the -- it's a variance
from the study. It's the information on glacial surge and sediment
input that apparently wasn't completed, but it's also the study that's
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been done that AEA undertook.
MR. DYOK: So if I could speak to the glacial surge part? We
wrote the glacial study that Gabe is doing. There's the literature
search that's part of, you know, his area of expertise, so he's doing
that. So he did the literature search, which was part of what was
required by the Federal Energy Regulatory Commission.
Then there's the part that's not part of the FERC process that
AEA felt that it wanted to do on its own.
MS. WALKER: I understand that.
MR. DYOK: We're doing that. The part about the glacial
surge with the sediment, that's more of a geomorphology question,
and so we turned that piece over to, you know, Tetra Tech to
undertake. They're still in the process of doing that.
They collected field data, you know, this summer to address
that particular, you know, issue. It wasn't a part of the information
contained in the ISR, but certainly is something that will be in the
Updated Study Report.
MR. FULLERTON: I don't know if this helps, but I -- we can
write this up and somewhere there was some other information
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yesterday that was needed and I think it said submit it by
November 15th.
So, we can write up our information on, there are conclusions
about glacial surge and submit it to -- on -- or on or about
November 15th, if that helps clear that part up.
MS. WALKER: Thank you.
MS. MCCRACKEN: This is Betsy McCracken with Fish &
Wildlife Service.
And I think that it's not clear to me whether this is in the
geomorphology study or not, but I think it's relevant to the sediment
transport and what I heard Mike say about the sand coming through
and mostly coming through, and the transport of that to the lower
river, and how that may be altered, and certainly the timing, if
nothing else, because that is what creates and supports the lower
river.
MR. MCLEAN: This is Dave, Dave McLean. Just a
follow-up question on -- relating to sedimentation.
Is there a description or a characterization of glacial changes in
major tributaries downstream, not just in the upper reach because the
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effects of long-term glacial change will affect land characteristics
and sediment yield in, of course, of the tributaries that have glaciers,
so it's a bit broader question than perhaps in just looking at very
specific questions related to the surge in the upper watershed.
MR. WOLKEN: Yes, I can field that to some extent.
Again, the glacial surge and the sedimentation, part of the
study is being handled by a different group, but as part of the
extended study that we're doing, we are looking at former glaciers
extend and area changes within the historical record up to present, so
we will be including that in our studies.
MS. LONG: Hi, this is Becky Long. (Indiscernible - over-
modulating) I want to give copies to FERC and AEA.
I wish I saw (indiscernible - over-modulating) about Gabe's
extended study, because he just said generally that it will be later,
outside -- well, actually I think you said it was after the ILP process
is done. Yes, I looked at it and so it left it in a very generalized way
and I'm glad to hear that it's going to come out. It was not mentioned
in the ISR that it will come out in 2015. So that's really good to hear,
because I think you will need that.
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Licensing participants consider this study data extremely
important to determine the feasibility of this proposed hydroelectric
project; specifically, will there be enough water in the proposed
reservoir from the Upper Susitna Basin runoff to provide 300 to
600 megawatts of hydroelectric power for 50 years, 100 years, and
up to a thousand years?
And it's important that we determine this for a thousand years,
because we said in the information we will use this summer that the
dam could go for a thousand years. So we're going to need this
modeling for a thousand years.
Now, this is -- it's tricky to comment on this study because
there's, like I talked about, there's a FERC component and an AEA
component, so it's kind of hard to talk about it and it's kind of hard to
explain.
So I think that the sedimentation people are saying that they're
looking at the glacial surge sedimentation. And are you finding that
it's insignificant? And -- because in the ISR -- well, let me go over it.
FERC said in their study plan determination to determine the
potential for changes in sediment and delivery rates to the reservoir
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as a result of periodic glacial surges. AEA proposes to review data
from previous glacial surges in the Upper Susitna River Basin
glaciers, as reported by Harrison & Humphrey, and evaluate the
sediment transport capacity of the reaches of the Susitna River
upstream at the reservoir.
If it is determined that the increased sediment load could affect
project operations, a sediment loading scenario accounting for glacial
surges would be added to study 6.5 geomorphology study.
This would include an estimate of reduction in the reservoir
life that could result from sediment being associated with periodic
glacial surges.
They followed-up, FERC followed up in their SDP analysis
with potential changes to sediment delivery from the Upper Susitna
watershed into the reservoir from glacial surges as proposed by AEA
is necessary and therefore am recommending approval of this portion
of the AEA's proposed study item.
This was not included in the ISR. I e-mailed Mr. Jayjack to
see. Is -- well, let me back up. In the ISR is a literature review, and
it's a really good literature review. I really enjoyed it. I understand a
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lot and it was very thorough.
But the ISR says the FERC component of the ILP is done, but
I respectfully disagree, and I think we need to clarify this.
This -- like I just said, FERC recommended that they do the
glacial surge study.
And also I think it's important, the unpublished study refers to
Harrison's 2012 Effect of Glacier Surges on the Sediment Regime of
the Susitna Basin that was submitted to the Susitna-Watana project.
Now, I understand there really is no study. It's just like
notebooks and stuff. But I think this data is important, so I hope
there's a follow-through on that.
And the remainder of AEA's 7.7 revised study plan is the
actual hydrologic modeling in order to develop water forecast models
for the proposed project. FERC does not require this. But FERC
does not mind that the applicant carries it out. (Indiscernible - over-
modulating) has explained this very well.
AEA states in the ISR that the data from these objectives
reported on in later years, and is not part of the integrated licensing
process. So now I know that it will be. So thank you for clarifying
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that.
So what if review did not meet the FERC SPD in terms of
(indiscernible -over-modulating) analysis of potential glacial surge
reservoir sediment delivery? If 6.5 is going to do that, I think we
need to put it in 7.7 because this is where it originated.
There was a few points of the literature review, 7.7 ISR Part A
did not answer the question; is the Susitna River considered a highly
glacialized catchment basin? Excuse me, I'm nervous.
Also, during periods of low flow, will the glacier's ability to
augment stream flow be diminished significantly and eventually lost?
This was not answered in Part A under 6.1, Evapotranspiration. That
section needs to make clear that increasing temperatures, growing
season length, and increased precipitation may not correspond with
increased water availability due to evapotranspiration. And this is a
direct quote that I took from NMFS's proposed study request in 2012.
There's been references to the 1981 to 1983 data on mass
balance and snow depths. The Susitna River Glacial Basin -- pardon
me, glacier runoff was analyzed by UAF's Geophysical Institute and
R&M Consultants for the Alaska Power Authority to develop water
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forecast models for the 1980s proposed two-dam Susitna hydro
proposal. This historic data we'll be used as part of the calibrations
for the hydrologic model for the current 7.7 study.
And I'm just wondering, is this science -- is this data
scientifically defensible, because there are limitations to this data.
And each -- this -- this was listed in the 1980s -- or the 1984 study.
Data from the Talkeetna Mountain glaciers and Eureka Glacier were
not included.
At best, this data is considered reconnaissance level with only
one measurement point for 50 square kilometers. A short, three-year
study duration gives little perspective into year-to-year availability of
water supply from the glaciers. The error is too large to say with
much confidence that the glaciers were in approximate equilibrium
from 1981 to '83. The accuracy is limited for mass balances of the
Susitna Glacier in 1983 because the only reliable accumulation data
was from the north facing basin of the main tributary.
The study indicates that during this time, roughly 34 percent of
the flow from above the Denali Highway is from the glaciers. Is this
credible data? Can we make this assumption?
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Stakeholders need to know when this material will be
presented, and I think you already answered this, that Gabe is
working on this.
So I think that's all I have.
MR. PADULA: Thanks, Becky.
So, yes, there's a case that Gabe is working on and Bill, the
other information, if I heard you correctly, by November 15th you
will have written up on the glacial surge (indiscernible).
UNIDENTIFIED MALE: Correct.
MR. PADULA: .....(indiscernible).
Any others?
MR. JAYJACK: This is Nick Jayjack, Nick Jayjack from
FERC.
So my understanding is the part that we required, the literature
review of the glacial surge analysis, that will be filed prior to the end
of this year. So November -- I think you said November 15th.
MR. PADULA: Correct.
MR. JAYJACK: Okay. And then just -- I haven't followed as
closely as some. So the second set of material that we did not
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require, when are you proposing to send that out to the group? Is
that -- is that the February -- end of February data, or February date?
MR. DYOK: That's correct. We just need to keep in mind
that that's a draft at that point. Gabe will not have a final, you know,
document. But he's willing to meet with folks as soon as he's got his
information to discuss it and that is something that AEA was doing
external to the ILP process.
MR. JAYJACK: Okay. Thank you.
MS. WALKER: This is Sue Walker with NMFS again.
I'd just like to, for the record, make it known that NMFS does
intend, and other licensing participants also intend to make a request
to FERC for a modification of this study.
We note that current NEPA standards, at least as set by current
practices and by recent case law, do require an assessment of the
effects of changing climate on a project of this nature.
Also current ESA consultation, also set by recent practices and
case law, require an assessment of changing climate. We're working
with the University of Alaska Fairbanks and with our earth research
science lab in Boulder, Colorado, to study the effects of climate on
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this project.
Although FERC did say that if there were unanticipated
changes in future climate, that the license could be reopened, we find
that changing climate is neither unanticipated nor a future condition.
It's certainly happening right now.
The literature search is very well done. We did appreciate
having that resource made available for our use. But we will be
making a request for a modification to this study, and it may be
unfortunate if we don't have the information that's being collected by
Gabe and Regine Hock, because I believe that work is being done
very well. It's an excellent study. That's what our climate scientists
agree, and I think it would be very useful if we could meet with the
climate technical work group, which we've only had a couple of
meetings. It was very, very useful to us, and we would ask again that
we be allowed to have that meeting. It would just be a couple of
hours of AEA's time and Gabe's time.
So thank you.
MR. PADULA: Thanks.
Any other comments that we haven't heard yet? I'd like to
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move us along, but if there's maybe one or two more.
MR. PHILLIPS: Is it on? Is it on? Guy Phillips, Kier
Associates.
Yesterday morning, I asked a question and was told I was
premature and so I tried to listen through the day to see if the answer
would emerge over the course of the day or the end of the day.
And then at the end of the day, I asked the same kind of
question around a much narrower and what seemed to me to be a
much easier topic which was (indiscernible - distance from
microphone) research.
The question was that I asked yesterday is how does all of this
fit together? I still have that question. So please (indiscernible -
distance from microphone) and I'm still confused in how this all fits
together and I'm a little concerned that it's premature to be asking
these questions. (Indiscernible - distance from microphone).
I think that it's fair to say that -- well, again, I'm the newcomer
on the block, so excuse me I beg your (indiscernible) for that. But I
think it's fair to say that we're all making the best effort here to
follow the path and build what I will call (indiscernible - distance
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from microphone) library. And in that library will be sort of a
collection of books, on what are the issues involved in designing and
building the largest dam in decades in a watershed of (indiscernible -
distance from microphone).
And in that -- on that path is everything from collecting raw
data, putting that raw data together in some fashion that characterizes
the watershed, which I was told yesterday was the stage we are in
and why my question was premature. But then as we develop that
characterization of the watershed, we're going to need to do some
modeling. And there's lots of discussion of modeling. There is
going to be some more discussion of modeling today. So there are
various stages in the modeling effort already, in which we are using
some models to characterize the watershed and in some cases we're
already making predictions.
In this trail that we’re following get to the library, it seems to
me that we have a (indiscernible - distance from microphone) process
that we’re following, more or less. That is, data collection that
includes culmination of data collected remotely, observational data,
and so forth.
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And then along that trail is the characterization work that I just
described that involves modeling. But that is very different point in
the process with prediction, and a lot of people are confused in this
room, I think, from the questions that I've been hearing between
characterization and prediction. And to the extent that we remain in
a confused state, we will continue to be fighting with the same
questions.
So if the answer to my questions yesterday is the same, that
this all comes later, and that's according to decisions made by FERC,
then I would make a plea to FERC to change that decision, to change
that outcome and move the process of trying to agree on what the
library looks like to earlier rather than later so that you see how all
this fits together.
I'll use one example that I already used with the Beluga whale
yesterday afternoon as another for us to try to understand how this
fits together. And I asked about the modeling aspects with the
belugas (indiscernible) and how it was tied in with the hooligan and
the connection wasn’t described but it was somehow going to be in
the same model.
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Further, on furthering the (indiscernible) content model, we
moved in from the characterization process into prediction, and
answers to my questions turned to (indiscernible) or want me to use
the modeling to predict the impact of reservoir operations on the
beluga whale habitat. And yet as far as I can tell, the mapping or
data collection around the beluga habitat isn't occurring.
So how do we fit that together later on? Or do we just defer
the point at which we argued about that to another time in this
process?
So if the answer is the same, I would encourage, plea with
FERC that (indiscernible) at which we are going to try to fit all this
together sooner rather than later. And we have two more days on
this kind of discussion and that will maybe make some kind of
discussion around that (indiscernible).
MR. JAYJACK: This is Nick Jayjack from FERC.
So I think I followed what you were saying, but correct me if
I'm wrong. The library that we're creating, right now we're at the
draft stage. It's the ISR.
The final library, if you will, is the USR. It will include the
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October 16, 2014
characterization, as you mentioned, of all of the resources that are out
there now. In some instances, it will have predictions, as well, as to
what potential effects could be, but really, in this process, the first
predictions will be the draft license application that comes after the
USR, but of course, prior to the license application being filed.
And I'm anticipating, as in all the ILPs we work with, that
that's where you see everything being put together for the first time
and a cohesive, you know, complete, more comprehensive look
being looked -- taken as to what potential project effects would be.
So it's all regulatory. The regulatory milestones, I don't know
what kind of freedom we have to move things around. But that's
kind of where we're at. Where we're at right now is we're in the draft
library stage, if you will.
MR. PADULA: Thanks, Nick, I appreciate it.
MR. JAYJACK: Yes, I understand the process and the
constraints within which you operate.
To the extent that we're trying to characterize this whole
dynamic (indiscernible - distance from microphone), it would be
helpful if we also characterize how we're going to use it. It would be
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helpful in that same characterization process to say we now have this
as a picture and I think characterizes it and here's how we're going to
build upon that to move to that place where we can actually make
predictions, rather than wait until the USR to be already making
predictions when we haven't really agreed upon the (indiscernible). I
think it'll save you time, save everyone frustration.
MR. PADULA: Thanks. We're going to move on.
MS. WALKER: Can I have just one more question?
Gabe, could you turn to your slide that has the graphs of
glacial runoff? The -- no. That one.
I think it's really important to know the question that we need
answered is on the bottom graph there of runoff over time.
We need to know where the Susitna glaciers -- water glaciers
are. And I've talked to other glaciologists and climate scientists who
believe that for Interior Alaskan glaciers, we're on the descending
loom of that curve.
I think that that's really the big question that we need
answered. Is that a question that your study is going to provide some
information on where we are located on that curve?
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MR. WOLKEN: That's right. I couldn't agree more with you.
That's a critical question for this. And what we hope to provide is
within these simulations of future runoff out to 2100, we should be
able to see what trend is in runoff and discharge throughout that time
period.
That at least within that 100-year period to give us an idea of
where we are on this curve. If there is a decreasing trend in runoff,
then that would be indicative of where we might be. If there is an
increase, then that would be indicative of where we might be.
Keep in mind, however, that's a 100-year period that the model
(indiscernible) for us, those simulations are restricted, they are
restricted to that particular import.
MS. WALKER: Okay. That'll be useful. I think that'll be
useful for FERC staff.
And FERC did note that their staff would find this information
useful in making their decision on any license application and I
believe that your study is ending, it's wrapping up now. So I'm
wondering if there will be enough information then for FERC staff to
use in their license decision, based on your study being completed
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now?
MR. WOLKEN: Is this a question about the timing?
MS. WALKER: The timing, and also whether your work will
be completed in your eyes.
MR. WOLKEN: We will be completing the study to the
degree that we can given the deliverables that we agreed to with
AEA.
MS. WALKER: Thanks.
MR. PADULA: Okay, we're going to move on. Here's Bill.
This isn't Bill's time but he assures me that he going to help us make
up some ground here.
UNIDENTIFIED MALE: Question – are we following a
different order than is shown on the website?
MR. PADULA: No, I think we're following the same
candidates that are on the website, the meeting website, the AEA
website.
MR. DYOK: I think his question is on the website, they list
the presentations in a different order than what's actually.....
UNIDENTIFIED MALE: (Indiscernible - interference with
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speaker-phone.)
MR. PADULA: Yes. We're going by an agenda here in the
room so there has been some reordering.
MR. DYOK: No, no, no, no. He needs to look at the agenda.
The agenda is actually correct. The way they just posted the
presentations doesn't follow the agenda.
MR. PADULA: Yes, not the order of presentations as they're
posted. There's actually an agenda that's posted, and we are
following that agenda.
So next up is --
UNIDENTIFIED MALE: Thank you.
MR. PADULA: Oh, did you state your name, please?
MR. HAMRON: John Hamrick.
MR. PADULA: Great. Okay. Moving on.
GEOMORPHOLOGY (STUDY 6.5)
MR. FULLERTON: Okay, Steve, thank you. Bill Fullerton
here.
And the rest of the morning we're going to be presenting the
geomorphology studies. And I say studies, plural, because there's
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two of them. There is the geomorphology study, Study 6.5, that I'll
be presenting and leading the discussion on, and then there's also the
fluvial geomorphology modeling study, Study 6.6, which Lyle
Zevenbergen will be presenting and leading the discussion on.
And these two studies have the common overall goal of
characterizing the geomorphology at the Susitna River and predicting
the effects of the project on that geomorphology. The difference in
the separation between the two is in the tools being used and applied
in that study. With the modeling study concentrating on the
development of the computer simulations and computer models, the
1D and the 2D bed evolution models.
The slide here has part of the objectives. There's actual -- the
11 objectives for the geomorphology study, I'm not going to go
through each one of these, but the very last one, you know, is the
integration of the fluvial geomorphology modeling study and the
geomorphology study. These -- in a way, they're not two separate
studies. They're very integrated. The folks working on the modeling
part, many of them are working on other aspects of the
geomorphology study. Again, the separation is mainly on the tools.
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There's 11 study components. Each one is related to or
corresponds to the study objective.
Also kind of give a little background. Much of the work in the
geomorphology study, 6.5, was conducted or started as part of the
2012 studies. And a lot of this is was used to help inform the
development of the RSP.
There are several variances in the -- associated with the
geomorphology study. I've highlighted three that we’ll discuss a
little bit. And there's actually three slides here with variances, of
which most of them are -- just deal with timing of material being
delivered, being somewhat delayed through the land access, and
other issues.
A couple of them are actually variances because we're
providing more information than was originally identified in the
RSP, so we're pointing that out.
But the three variances I'll discuss, two of them are highlighted
on this slide, and they both deal with the data that was being
collected by the USGS, the sediment transport data.
The first one deals with the bed-material sampling. It was not
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conducted in 2012. There's been flex samples at each or near each of
the locations where they've collected their discharge and sediment
transport information. Due to the high flows, they weren't able
to -- there weren't exposed bars. They couldn't do their pebble
counts.
This is not an issue because we've done in the geomorphology
study extensive bed-material of sampling throughout the Susitna
River from the upper river, down through the lower river and
tributaries. So we've got a good characterization of the bed material
without that information.
The second variance was -- that dealt with the bed-load
sampling for the Susitna River at Tsusena Creek, and that was
terminated after 2012 due to logistical and safety concerns.
Again, we don't see this as an issue because we have alternate
means of determining the bed load at that location and they did
continue the other -- the suspended sediment sampling as well as
their discharge or the gaging station.
The last variance I was going to discuss is associated with the
collection of aerial photography. Originally it was intended that
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aerial photographs in the middle river would be collected at three
different discharges. These would be used to develop habitat area
versus discharge relationships in the middle river.
We have only collected aerials at one target discharge, the
medium flow, 12,500. Again, the other -- this task of the use of the
three aerials is kind of a carryover from the 1980 study where they
used that type of a relationship to help determine the effects of the
project on the habitat area.
But with the approach we're using now in 2013, '14, '15, to
have focus areas where we have complete topography, the
bathymetry, we're running 2D models. We can determine at any
discharge the areas associated with -- the habitat areas associated
with that discharge. So we don't need the aerial photos to do the -- to
develop the habitat area versus discharge relationships.
The rest of -- as I said, the rest of the variances are mainly
dealing with timing.
Those are the results of the ISR. I’ll just to go through this real
quickly. We've submitted back in March -- or February and March of
2013, seven different technical memorandums that represented a lot
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of our work that was done in 2012 and early 2013.
In the ISR itself, we had four very substantial appendices or
basically technical memorandums in themselves and we've also
updated our geomorphic reach delineation and characterization and
filed that in May of 2014.
And just a few slides here highlighting some of – since we
can't show information from all 11 study components. This is just
some of the sediment transport relationships that were developed
from the data the GS collected in the '80s and also 2012, 2013.
This is incredible information. A lot of rivers were studied.
Just don't have the opportunity of having data that spans this time
frame or as at many locations as we got them.
This slide just highlights one of the findings from the
geomorphology study and the field work and integration with the
modeling effort, and that's the succession model that Mike Harvey
developed to characterize the current condition and the relationship
between the river stage and the various geomorphology surfaces.
The takeaway from this was that we found that the ice
influenced -- the ice processes influenced the development of the
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surfaces, it's not just purely fluvial driven.
And the last part here is the decision from the ISR on the six
tributaries that were selected for study in the reservoir area as in
conjunction with areas of (indiscernible). We're not going to go over
the information from the -- since the ISR, the 2014 efforts.
If you do want -- we talked yesterday, Lyle may discuss the
modeling behind the decision on extension of the model or not
extending the model below Susitna Station.
There's -- and going forward, there's no additional
modification other than just continuation of the variances that we've
identified for 2013.
The last couple of slides just show the status of the study. If I
could tabulate this with 11 components, it's a bit difficult. But we
have three columns showing the study component, what was
completed to this point in time, and then what's planned for
completion. And it goes over each one of the 11 studies, and to kind
of highlight things, the regular font is work that we've completed. A
substantial effort, but still have a substantial effort to do, such as the
component 6. The component 7 is one that we've basically
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completed and it's noted with the italics.
And then the bold are studies that primarily are being
undertaken in the second-year study.
And that's -- I'm ready for questions and discussion.
MR. PADULA: Thank you, Bill. And there's 12 minutes.
Great job.
MR. FULLERTON: A record for me.
MR. PADULA: I know you've got a lot of material to cover.
So we're open for questions for Bill for his portion of the
work. Again Lyle will be up just after the break, so if there are
questions for him, please hold those.
MS. GLASS: This is Dara Glass from CIRI. And, Bill, I'm
sorry; I cannot remember why the study is not going beyond Susitna
Station.
MR. FULLERTON: So the study is not going beyond Susitna
Station -- well, this study actually does go beyond Susitna Station.
It's the models that we're not extending beyond. We are doing other
geomorphic characterization and that's downstream all the way to the
mouth.
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MS. GLASS: But what's the reasoning behind it? Is the next
study going to deal with that?
MR. FULLERTON: Yes. That's what Lyle will address. I
think it'll be more cohesive.
MS. GLASS: Nobody brought me my Pepsi, so I'm a little --
MR. FULLERTON: Again, it's a little confusing that these
two are separated to begin with.
MR. MCLEAN: This is Dave McLean from Northwest
Hydraulic Consultants.
So because the sediment modeling and the sediment --
geomorphology studies are very integrated and because we have
questions on how the two are going to be tied together, how you're
going to use different methods to check different predictions,
actually, I'd be interested in hearing the modeling presentation now
and then we could give questions on both together rather than just
talk about geomorphology and end that and then talk about modeling
because I think they are very related.
MR. FULLERTON: I have no objection. I think that's a
good --
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MR. PADULA: We wanted to get through Bill's piece, go
right to Lyle's piece, and again, if you have questions then that really
relate to the two and how they interact, we'll be right there.
Any other questions just specifically for Bill on his material?
MS. WALKER: Yes, I have one comment that relates to
variance in the literature search. Delaying the literature search until
after the study tasks and data collection are substantially completed
is really unfortunate because it reduces the opportunity to incorporate
really important lessons that have been learned from other projects
into the study program and the study design.
Normally the literature search would be conducted near the
start of a project so that those -- that information could be brought in
and those lessons could be applied to this study. It doesn't seem to be
cost effective to delay this.
And the reason given is for coordination with the riparian
instream flow. I would think that study could benefit from the
literature search being done sooner rather than later as well.
MR. FULLERTON: Well, the literature search has been
completed and the technical memorandum was submitted.
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MS. WALKER: Is that something then we'll be receiving by
November 15th?
MR. FULLERTON: It's -- should be posted now because --
MS. WALKER: Because that's really good news.
UNIDENTIFIED VOICE: It's not posted now.
MR. FULLERTON: Oh, I'm sorry. I thought --
MS. WALKER: That was a question. Is that information then
that we can expect to receive by November 15th?
MR. FULLERTON: Yes, we'll have that by November 15th.
MR. MCLEAN: So the follow-up question would be, has
what you -- the lessons that you learned from that literature review, is
that reflected in the ISR and your study planning and the whole
program that you've launched on this whole project?
MR. FULLERTON: Yes, because the literature search was
being conducted from early in the project. We've been reviewing the
literature.
We had submitted, I think with the initial -- the part A of the
ISR had a bibliography with all the references in that. So what's
gone on in the -- since then was kind of coordination -- more
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coordination with the riparian and actually grinding it up and
synthesizing information.
MR. MCLEAN: But there's no actual sections that describe
lessons learned or case studies from previous projects? That is not
visible, at least to me.
MR. FULLERTON: In the ISR?
MR. MCLEAN: Yes.
MR. FULLERTON: No. We don't have that information in
the ISR. But some of the information such -- a lot of it on the ice
processes, influences, like that, helped Mike a lot with the field work
that was conducted, and also help Kevin Fetherston, who is
conducting the riparian study. So we've been taking advantage of
that information and that was in that literature, whether it's reflected
as lessons learned in the ISR or not.
MR. MCLEAN: Thank you.
MR. DYOK: This is Wayne Dyok. If I can just make a
comment?
Maybe the agencies and others here can help us out because
one of the challenges that we've got is in this series of tech memos
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that we prepared to try to help, you know, folks, to give you current
information,. I get criticized because we've got so much information,
so we actually held back part of this because of - when we got the
feedback, we were told, "Oh, it's overwhelming."
So do you want us to give you a hundred pages of maps?
Because I think this is really important for us. Part of the goal here is
to give you information, and I don't want this coming back to say,
"Hey, you gave us so much information we couldn't deal with it."
Because part of the challenge that we have now to get ready
for the next field season, we don't get first determination until
April 22nd. We need to be out there potentially on May 1st. And if
there are some significant changes, it's going to be a challenge.
So I'm happy to give you, you know, information, but I'd like
for us to talk about how that information is going to be used and
make sure you get it in a timely fashion. So could we work together
on information that we need and when you need it and the kind of
level of information, I think that would help all of us as we go
forward.
MS. WALKER: This is Sue Walker, with NMFS.
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This information, not having it now is a variance. We would
have expected it in draft, the literature search. So however long it is,
you know, we would have expected it earlier, but now is certainly
better than later.
MR. DYOK: And I'm not going to debate a variance or not
here with you. We will provide this by November the 15th..
MS. WALKER: List it as a variance.
MR. KRISTANOVICH: This is Felix Kristanovich with
Environ (indiscernible) and I would like to raise the point with
integration of this study with other studies.
Like for example, the model integration (indiscernible)
diagrams showing how one study relates to another study. I know
that (indiscernible) [the effects in the lower river]. For example, if
you turn to pages 20, 21, it says (indiscernible) results. I would like
to know more specifics, you know, how specifically parts of this
study are going to be used (indiscernible - over-modulating) for
example with respect to changes in the ice process model, or
basically the relation of all the other models, how does this all fit
together. I don't know whether to (indiscernible).
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MR. FULLERTON: Well, I think the presentation that Lyle
provides pretty much concentrates on -- within our study but we can
talk about that. I think it would be good maybe we can talk about
that after Lyle does his presentation and, you know, it's -- Felix's
question is along the same lines as Dave's, so we can kind of address
those or have a discussion all together. But I think it would help to
have Lyle's presentation.
MR. JAYJACK: This is Nick Jayjack from FERC. If you all
don't mind, I'd like to go back to Wayne's question just a few minutes
ago, because I think it's really pertinent to the process.
I think Wayne was speaking more generically than just about
this study. I think the question's a good one. We were sent over
1,500 pages of additional information that, as Wayne stated, I think
he felt would be helpful to the process.
And so we -- you know, for some it was difficult to have that
kind of information, the volume of that information, prior to this
meeting, including us, I will admit. It was a lot of information.
But I see Wayne's point, that having that information could be
valuable, but he's kind of walking a thin line as to do I provide it or
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do I not provide it. So I think it's a worthwhile quick discussion to
have what do folks want. Do you want information and -- for all
intents and purposes that's in real time, or would you prefer that the
information be held back?
I'm not talking about necessarily information that was required
by the study plan determination. I think it's more generic than that.
The studies are ongoing. They don't stop. They don't stop for
timelines. They're -- you know, information is coming all throughout
this process.
So I'm just curious to hear what folks have to say about should
he hold off on the information until we actually hit a
mile -- technically a milestone, or is it better to receive the
information a little bit more real time?
MS. LANCE: This is Ellen Lance, Fish & Wildlife Service,
and I'll speak for the Fish and Wildlife Service right now.
But I think we had discussions with Wayne about continuing
the technical working group meetings to share information and I
think that would be really valuable going forward, as we're starting to
get into the meat of this information. And I think that would be a
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really helpful way to share information that's not necessarily in a
formal manner.
And also, with regard to the many, many pages of new
information, I can understand sort of wanting to pulse it out to us.
We just need a heads up so that we can prepare for it, because you
know, receiving it a month before and expecting us to comment on it
isn't a reasonable expectation.
So I can understand that you need to provide this information,
we just need to have a good heads up that it's coming. So knowing
that we're getting more November 15th is very helpful. Thank you.
MS. WALKER: This is Sue Walker with NMFS again, and I
concur with Ellen.
I'd add, though, that in addition to knowing when we will
receive information, we would like to know what we're going to
receive in as much detail as possible. That's been a very frequent
request of the services. What are we going to get? What's it going to
look like? How long is it going to be? And we need that detail.
That has not been information that we've received, even this time.
We were told five to ten pages of information in 20 or 21
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reports. We ended up with over 1,800 pages and less than two weeks
of expected review time. Having had that pulsed out, staggered out,
that would have been much easier, I was hoping, and easier to plan if
we knew what was coming. So yes, give it to us when you have it.
Stagger it. We can't work on it all at once anyway.
MS. STEELE: This is Marie Steele from the Alaska
Department of Natural Resources.
I do agree that having a heads-up that the materials coming
and what it comprises of is very important, because we have -- the
reviewers have a responsibility to get their feedback to you in a
timely fashion so that if they can schedule a time, that would be
great.
I do want to reiterate that the reviewers have a responsibility to
review this material in a timely fashion and get the feedback to you.
I do say that there are reviewers on the State side who have reviewed
the technical memos and they are frustrated that this information, this
timely dynamic information has not been discussed at today's
meeting. So I think there is a fine where you have those that are able
to assimilate the information in a timely manner and those of course
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feel over-whelmed.
MS. LANCE: Ellen Lance, Fish & Wildlife Service.
Just wanted to get back to your question about reviews in time
for you to prepare for the field season. And we do intend to look at
what we have and try to prioritize our comments to you so that you
can prepare for the next field season as much as we can.
MR. DYOK: Yes, thank you. That's much appreciated. And
maybe if we could take a few minutes tomorrow afternoon, I know
people are probably going to be in a hurry to get out of here, but just
to go through the information that we're going to be providing by
November the 15th, so we all can be on the same page.
I understand where you're coming from, you know, Sue and
Ellen. You want to know what you're going to get, when you're
going to get it, kind of what it's going to look like. I appreciate that.
MR. PADULA: Any other questions on this topic?
MS. WALKER: One final word. As Ellen touched on the
need for technical work groups, I think that would help us greatly to
process this information very quickly if we had technical work
groups that were really work groups where we could sit down and
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have discussions and not be just given a presentation, but actual
interactive technical work groups.
The licensing process has evolved to the point where more and
more of that is happening and that's been extremely helpful. So I
would encourage that to happen in this short time frame that we have
before us now with the new schedule.
MR. DYOK: We'll ask Lyle to be very, very, very terse as he
goes forward with his modeling presentation. I think, you know,
we're hearing from everybody here that they want discussion, so let's
presume that they've read the materials that are in the ISR and
they've looked at your slides and let's go forward from there.
MR. PADULA: Lyle, are you all set?
MR. ZEVENBERGEN: Yes. Thank you.
MR. PADULA: Let's do a 15-minute break. Lyle will get set
up, and hopefully we can have a really overall discussion of
geomorphology.
(Off record.)
MR. PADULA: It's time to get started. I wanted to make one
comment. Just this one comment.
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I know this is challenging for everyone, and it's got to be
amazingly challenging for folks who haven't been in the process the
entire time who knows all of this history of information and where
things are.
So with regard to some of the questions about model
integration and essentially do we know where we're trying to get to
and are reflecting the right information and how do the models work
with one another. There is a pretty good write-up, and it's -- for
those who want to write this down, in the June 8.5 ISR, that's the
instream flow ISR, Appendix N has discussion on model integration.
So for those who are looking for kind of that basic roadmap of how
this is all intended to come together, there is a good write-up there.
It's basically based on the proof of concept work that's been
done. So again, I would -- for those who, again, maybe haven't been
with us, and don't realize a lot of that thinking been done, I would
refer you there.
And, again, if that generates more questions, that's great, but I
think that's a good place for folks to start.
So thank you. And I'm going to turn it over to Justin, who's --
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MR. ZEVENBERGEN: I touched the computer and I broke it.
MR. PADULA: Oh, my gosh. It's bad when the modeler does
that. I'm worried.
All right. A few seconds while we boot the computer back up.
MR. CROWTHER: That's a different computer.
FLUVIAL GEOMORPHOLOGY MODELING BELOW WATANA
DAM (STUDY 6.6)
MR. ZEVENBERGEN: Well, I can say that what I'll do is I'll
go very lightly on the ISR material, because that, obviously, you've
had time to review, and just touch on some of the changes,
modifications, that sort of thing, very briefly.
And then since there's been a lot of questions on the decision
point and that sort of stuff, I can bend these back into that
information and hopefully answer a lot of questions that have been
coming up.
The other side of things is that with the range of studies and all
of the integration that does need to take place, that naturally you do
have questions regarding a component that affects several studies,
but you don't get to hear the presentation until the second day or get
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to discuss that until the second day.
So I appreciate your patience. And hopefully we can get a lot
of your questions answered.
As Bill said, the geomorphology and geomorphology
modeling studies are intertwined. They're really one big study, so the
interaction is continuous between those studies.
And the -- so we are -- we're always looking at how does the
modeling identify issues and then how does the observation inform
the modeling, and that sort of thing. So there's a continuous
integration between these two studies.
And so to call it formal, you know, it's not like we sit down
and have weekly meetings or anything like that. It's always a
continuous discussion, and then the modelers versus the field crews,
and then the interaction between those.
MR. ZEVENBERGEN : It's slow. I really did break that
computer.
So our overall objective, overriding objective, is to
characterize the river and to make predictions as the -- as we move
forward. So the -- you want to characterize the response of the river,
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identify what the primary processes are, and use the -- the models to
make the predictions in the -- into the potential project effects.
There were no variances in this study. The only variance
that -- the only difference really was in the timing, getting access to
getting data collected in certain areas, some CIRWG lands, and that
sort of thing.
That really wasn't a change, because we didn't anticipate doing
all of our data collection in one year to begin with, so we were
counting on multiple field seasons, and so that access was not an
issue for our data collection.
In terms of our results, in the bed-evolution model
development that was reported in the ISR, it focused really on the
selection of the models. We wanted to select the best models for the
project, and our models became either one-dimensional modeling,
reach-scale modeling from Watana Dam down to PRM 29.9.
And the -- that model was selected as the Corps of Engineers'
HEC-RAS model and they were very happy with that choice.
HEC-RAS version 5.0 is a beta model. The Corps of Engineers was
very interested in having us apply this model to the project, and so
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they've been very supportive of that.
MR. CROWTHER: You can go ahead – we’ll get it working.
MR. ZEVENBERGEN: Okay, great. Thanks.
So I'm really up on slide 5 here. There you go.
So the modeling itself was in process during the ISR,
development of the ISR.
The two-dimensional modeling that we're doing in the focus
areas is related to detailed sediment transport and detailed hydraulic
information at the focus areas. And that model is the Bureau of
Reclamation as their SHR-2D model was the model that we selected
for that.
And again, we have models that were in various stages of ten
focus areas, so some of the focus areas have a small amount of work
done, and then some of them, like focus area 104, was in process at
the time of the ISR.
Study component 1, in terms of the model development, I
really would like to identify where all of our data comes from. It
comes from numerous studies. You can see Study 8.5, the cross
section, bathymetry data. We get substrate mapping from Study 8.5,
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water surface elevations. So really a lot of data has been collected
for both model calibrations and model inputs that you -- for our study
and for other studies, as well.
Study 7.5 was stage hydrographs, and then the work that we're
jointly doing between geomorphic -- geomorphology and the
modeling.
Winter bed sampling, the very last bullet there, is reported in
the ISR, but that was a preliminary -- just a study to see if it was
possible.
Study component 2, the results include -- we selected the 50
years for our analysis that we're going to run with our reached model,
and then we selected representative wet, average, and dry years.
Those are for the focus area models. And that is contained in
Appendix E, those two items, the 50 years and the representative
years.
There was a fluvial geomorphology modeling approach tech
memo that was produced in June and then the proof-of-concept
meeting, modeling that was done for that, and that's at focus area
128.
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This really does show some of the results there for that
proof-of-concept meeting and shows the interaction that took place at
that meeting demonstrating our ability to provide the hydraulic
information that instream flow fisheries needed.
The two technical memorandums that are -- since the ISR are
detailed winter bed material sampling and the decision point.
And I think we can just skip to slide 14.
Two modifications that were significant, one of them was
including groundwater inputs into the focus area models. That was
identified as a very significant item from the habitat standpoint. And
then -- so that's in addition. And a deletion is to not include Pacific
Decadal Oscillation as part of the distinguishing features for the
hydrology.
And then on to Slide 21.
Okay. So this is a future decision point. It's identified in the
ISR, and basically it's how much 2D modeling will be done at each
focus area. And so this describes, you know, under what
circumstances would we curtail some of the 2D modeling at the
focus areas if they're not providing additional useful information.
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Status and -- is -- we've really collected the vast majority of
the data for the modeling. I don't anticipate needing any more data.
We have characterized groundwater in flows in some of the lateral
habitats, which is very useful.
And the LiDAR's completed. 1D modeling, initial models
have been completed. 2D modeling, some models have been
completed and some have -- are in development. And there will be a
tech memo on that fluvial geomorphology modeling coming up.
Planned activities for 2015 really can be summarized into we
will finalize the 1D models; finalize as many 2D models as we can
given the available data; and fill in any data gaps that we identify as
we put together the models.
So model integration, there have been some questions related
to that. We are -- the planned integration -- and we can't really
integrate the models until we have reached at least a certain state, so
although we've been discussing how we're going to integrate the
models, we haven't actually done that model integration yet, because
the models are still in process.
But the reservoir trap efficiency from water quality is
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something that we'll need to look at. Ice break-up surges from the
ice processes modeling is an important factor that we were talking to
Study 7.6 on.
Groundwater in lateral habitats, that includes both Studies 8.5
and 7.5.
Large woody debris is really part of our study, but it needs to
be integrated into our modeling.
The turnover analysis will drive a lot of the information related
to production of large woody debris, and also sediments and future
change, and floodplain accretion with Riparian Study 8.6.
So those are the primary levels of integration.
So, if I touch this, hopefully I don't break it. Let's see here.
Page down.
So questions? I'm sure that took longer than I was supposed to
have.
MR. DYOK: You did fine.
MR. ZEVENBERGEN: Good.
MR. PADULA: So you've got Mike, Lyle, and Bill, very
integrated (indiscernible). So no, feel free, questions (indiscernible).
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MR. MCLEAN: It's Dave McLean.
So my question would be -- if I can start off with an
observation that I think most scientists would agree that a lot of these
processes that govern channel stability, changes in channel pattern,
complex sedimentation interaction between fine and coarse
sediments, these are all fairly imprecisely understood and so there's a
lot of inherent uncertainty and predictions. I think that's a given.
And yet, I mean, we have to try to come up with predictions
and I realize the challenge that your teams are facing. It's quite a
complex problem to deal with.
So some people advocate trying to use a variety of techniques
using geomorphic methods to provide independent estimates to
compare it with modeling estimates and trying to provide checks and
balances on these different levels of predictions.
And you talk about integration, so I guess I'm curious to know,
could you give some examples of how you are planning to make -- or
are you planning to do those kinds of independent verifications or
checks with perhaps simpler methods than a 2D model, but that will
help validate these results, and will you be trying to give people a
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picture of what the uncertainty is in these -- in these answers that
you're coming up with?
Because that seems to me almost as important as the answer
itself. So it's more of a philosophical question, but I thought I'd start
with something like that.
MR. FULLERTON: Just one of the first things, which I guess
in terms of -- is this portable here?
Okay, so one of the first things we've done is a comparison of
some of the model results with what we see in terms of level of
response in historical cross sections. So as part of the
geomorphology study, 6.5, we have a tech memo which I believe is
quite a historical cross-section comparison, where cross sections that
were closely located between the 1980s study and the current study
were compared.
Also we used those cross sections to develop a profile. And
then when Lyle's -- now, we don't have the luxury of having the
complete set of data that you could run from the 1980's and compare
-- you know, start 1980's and run the present, the response.
So what Lyle did, and maybe you can expound on it, when he's
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looking at some of the initial runs, and Lyle has compared the level
of response and the direction of the response when he ran the 60
years of -- or 50 years of historic record.
Actually, if people were interested -- I mean, there's a tech
memo in one of the slides that I had that was 2014, after the ISR
showed one of those cross sections, and -- a profile, which it's kind of
hard to see anything from the scale on the slide and stuff. But that's
one thing.
And then Lyle's got some interesting slides. I think that one of
the things I talked about that we were going to be doing is
developing the sediment transport relationships in Study 6.5, which
in places were used as the supply to the system from the upstream
and the tributaries, but also it's at some of the intermediate points
Lyle did comparisons of what we were getting from the model in
terms of transport with what had been majored over in -- in the
1980's and currently by USGS. And that slide is in your presentation
to -- do you want to pop that up, and --
MR. ZEVENBERGEN: I do. But I mean, I think I'm going to
also add to this question a little bit more, too, and it does refer back
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to something that you said in your presentations, that we had
different tools.
We have the modeling tools, and then we also have a lot of
other process relationships that we are looking at, whether these
process relationships are related to grading, channel grading, channel
form, channel plan form, you know, whether the modeling is going
to tell us something that is incongruous with what the observed
features are out there, and so we are doing those kinds of
comparisons. So we do have different tools, but we are cross
checking the modeling versus the observed information.
MR. HARVEY: Maybe I can just weigh in, too as sort of a
baseline.
I've spent my 40-odd-year career being a cynic or a skeptic
about models. That's my job on this thing, is to look at the modeling
and see if it actually makes sense with what's out there.
We spent a lot of time out on the ground over – nearly three
seasons now, pretty much covered every bit of that river and so we
have a really good handle as to what's out there. And, you know, as
I’m sure you’re aware, if you look in the literature.
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Most -- well, you can make a generalization that most rivers
are singular, that basically responses of a given river to a project are
not necessarily transferable, because in essence, each one has its own
set of conditions.
In fact, the dam literature will tell you that, that it's very
difficult to predict, based on what's happened elsewhere.
And so I think from the perspective of field observation and
modeling, I think we have a pretty good understanding of what's out
there, and, you know, and probably Lyle’s (indiscernible) with his
modeling because we talk about it and say that makes sense or it
doesn't make sense for what we're seeing out there.
So to try and answer your question there, yes, we're going
backwards and forwards. We're looking at modeling, and we're
looking at observation as well.
MR. MCLEAN: Yes, I'm sure you are, and I'm sure any team
would do the same.
I guess my question was: Are you actually going to try to
make formal analytical calculations and predictions using
non-numerical methods to come up with a separate answer so that
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you can try to -- as an independent check on just the modeling result?
So it's one thing to say while we -- you have a vast amount of
field experience, and it makes sense intuitively. but, I mean, there's
also a more formal methods that can be done that give you some way
of bracketing the predictions.
To me -- I mean, lots -- you can make -- now that we have
powerful computers, we can make tons of predictions. How are you
going to put the error bars on your predictions?
MR. ZEVENBERGEN: Well, part of that process is doing the
turnkey analysis. And we will be looking at -- again, with the
models, looking at changing inputs, seeing how the system responds.
Is it sensitive to the input or is it insensitive to the input? And we'll
be doing that.
We'll also be comparing the results from the different models,
and they're extremely different models in 2D versus 1D.
But then in terms of calculations, again, we have the
information going back to 2013 tech memos, where we have looked
at the sediment transport relationships, looked at the combinations of
existing conditions, periods of time, and that sort of thing, to get
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predictions of how the system is working right now, how the system
could respond, put some -- like you say, put some error bounds on
that.
And so the -- if you look through, I think, the range of tech
memos, at the attributes related to sediment turnover, geomorphic
mapping, and that sort of stuff, but that is the basis of comparison for
a lot of the modeling that is taking place now. So --
MR. HARVEY: Well, you obviously have something in mind,
in terms of your non-numerical testing. I'm just curious as to what
you think.
MR. DYOK: Use a mic.
MR. HARVEY: I'm sorry. Obviously, you have something in
mind in terms of a non-numerical way of testing the modeling
results. And I'm curious as to what you might be suggesting there.
MR. MCLEAN: Well, it's more of a philosophy in a way than
speaking about a specific. But I guess I'm thinking of the kinds of
work done by people like Kellerhals and Church over periods of
decades on -- and essentially, I guess, I'm borrowing their -- some of
the work that they have produced and some of the things that they
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have advocated for studying the effects of large projects on big river
systems. So in a sense, I need to acknowledge that I'm reflecting
their philosophy on how to study a river.
In terms of specifics, I think the -- what you call a turnover
analysis, I would think of more of a sediment budget or a channel
zone sediment budget analysis. I mean, that's one way of coming up
with sediment loadings or transport rates that's somewhat
independent of the bed-load measurements.
So that, to me, would be certainly one of the more critical
aspects for looking at the bed loads. So of course the bed load is a
very tiny fraction of your overall sediment loads. I mean, it's like 1
to 3 percent or something. I can't remember the number. It's a tiny
fraction. And yet, of course, it's so important for habitat, for building
the habitat of the -- that's used by fish.
So understanding that bed load seems to me very critical and
the data for characterizing it is so -- such a huge range of numbers
that you're relying on, like the rating curves that you've put into
these -- you know, there's a scatter of the usual two orders of
magnitude. I saw one -- for the bed-load rating curve, at a discharge
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of 15,000 CFS. The bed load could be anywhere from 100 to 10,000
tons per day. I mean, that's 100 -- yes, 10,000 tons per day.
So if you can overcome that -- I mean, that poses a huge
limitation on your predictability. And sticking a logarithmic rating
curve through a scatter of that magnitude is a very brave effort.
But -- so finding other techniques that can allow you to come
up with predictions seems, to me, very important. That's what I'm
trying to emphasize.
MR. ZEVENBERGEN: So I think that's a really good segue
into the modeling results and --
MR. HAMRICK: We’re not seeing the full slides.
MR. ZEVENBERGEN: Would you go to Slide 12, please?
Is -- is --
You don't see the transport slide, John?
MR. HAMRICK: The left -- I think the right side of the slide
is cut off. I see the slide but only about two-thirds of it. Yes, that's
much better. Thank you.
MR. ZEVENBERGEN: Is that better, John?
MR. HAMRICK: Yes, very good.
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MR. ZEVENBERGEN: So this slide does show the USGS
bed-load data that was, what, in the '80s and more recently, and it
does show a very large amount of scatter. And this shows Gold
Creek, Sunshine, and Susitna Station.
The large amount of scatter isn't because of data collection
errors. It's natural scatter that you would expect in this kind of a
system with all of the complexities of the different sediment inputs
from the major tributaries and the -- just the natural processes of the
transport. So the -- we do put in a -- as you said, a logarithmic rating
curve as a boundary condition to the model, at the sediment supply,
and yet the model is also providing us with a lot of that scatter at
Gold Creek, the majority of the scatter at Sunshine, and the majority
of the scatter at Susitna Station.
So the models are very complex models in the processes that
they are simulating in terms of the hydrodynamics and in terms of
the sediment movement, sediment storage, changes in the substrate
through time. And so this is an example of the kind of data that you
just don't have in most projects.
And so the -- the data that we're -- none of this data was used
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as the model input. You know, this data was only used for this kind
of comparison, and also to develop the loads -- the long-term loads,
the long-term sediment yields from the basin.
So this is really, I think, a very good demonstration that the
modeling process is incorporating a large range of the natural
variability.
MR. MCLEAN: I can't read the scales, but is this --
MR. ZEVENBERGEN: The scales are --
MR. MCLEAN: -- is this the gravel load or is this the bed
material load or the a bed -- gravel bed load? I wasn't sure --
MR. ZEVENBERGEN: This is the -- this is the total bed
material load. So, all --
MR. MCLEAN: So it's an suspended sample plus the gravel
load and the suspended sand load is, of course, much, much greater
than the gravel load by fractures of a hundred or ten or --
MR. ZEVENBERGEN: Yes.
MR. ZEVENBERGEN: Yes. So the gravel loads are dwarfed
by the sand loads. So that's why this next slide is, I think, really
important. I'm doing page up and page down, and -- okay.
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So this -- this next slide is also important. So it's not just the
loads that we are -- that we're comparing, but it's the transported
gradations. So again, this is all of the USGS data, and it shows,
again, a lot of variability. The -- and so the scales here are going
from zero to a hundred percent in terms of the -- the sediment
gradations.
The X scale is a logarithmic scale that goes from the very fine
sand up to very coarse gravel. And so the -- this is showing at Gold
Creek, at Sunshine, at Susitna Station that -- at Gold Creek, you have
about 99 percent sand and 1 percent gravel on average and the model
is also producing pretty darn close to 99 percent sand, 1 percent
gravel.
But Sunshine is a bit different where the -- you know, you see
a lot more scatter there because we have the influence of the Chulitna
as a highly variable sediment supply and very major sediment
supply.
And the Talkeetna is also a sediment supply that's, in some
respects, greater than the middle river of the Susitna. And so
very -- highly variable measured loads occurring from the
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modeling -- or from the measurements. And again, modeling is a red
line for the model and a black line for the -- for the measurements,
for the average of the measurements.
So again, a much larger percentage now. We're talking maybe
5 percent gravel and 95 percent sand at this location.
Moving down to Susitna Station, we see a much tighter range
there. Definitely dominated by sand, probably on the order of
3 percent gravel, 97 percent sand. So that's -- is showing how the
system is responding, and the model, as well.
Now, the models are -- they are our initial models. They do
not incorporate 2014 survey, so they were based purely on the 2012
and 2013 survey data. So the models aren't complete by any stretch,
but -- but these are the results of our initial model with these
comparisons.
So I agree with you that the gravel is an important feature of
the transport, but the -- but it is a sand-dominated system and
especially in the lower river where there are very few areas where
you see traditional (indiscernible) or that sort of thing. It's really
much more of a sand-dominated system through the lower river.
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MR. MCLEAN: So I guess this sort of brings up a question I
also had. In the studies in the '80s, there was a lot of discussion
about the supply limitation, about the seasonal history, the variability
over the flood hydrograph of sediment loads.
And there was a question really on which fractions of the
sediment are supply limited and which fractions are wash load,
which are really bed material load. I guess I got a bit confused
reading your text because you sort of never really specifically
defined how you -- how you came up with what is your criteria for
distinguishing wash load and supply limitation and bed-material
load.
But I'm not even sure that the sand in some reaches of the river
would be characterized as a bed material load. I mean, it may be
supply limited. If you look at the bed material samples, the sand
fraction in the gravel-bed reaches of the river, you know, it's very
small.
So say it's 3 percent of the -- in the bed -- bed material samples
and yet it's accounting for ninety- -- as you say, 90 percent of the bed
material load. It's odd to think that it's -- all of the sand is actually
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behaving as bed material load and in fact, maybe some fractions of
the sand are really wash load. Some fractions are truly interacting
with the bed as bed material load. I mean, the distinction of bed
material load just on the sand -- definition of sand seems somewhat
arbitrary. I know it's commonly done, but usually there's some
logical assessment of how you define that.
MR. ZEVENBERGEN: Well, and I agree and I think that we
really have two rivers here. You have the middle river and the lower
river.
The middle river, from what I've seen in the field from the data
that we've collected in the sediment measurements of the -- that the
bar heads, the winter bed sampling, all of our field measurements,
and really digging into the available data, really indicates that
virtually all of the material being transported in the middle river is
throughput load, kind of a wash load condition. The sand
certainly -- the -- and the gravel sizes are probably supply limited, as
well, in the middle river.
The -- in the lower river, the system changes dramatically,
where the interaction with the bed is probably occurring through all
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of the sand sizes and gravel sizes. So a huge change at the Three
Rivers Confluence, and because of that, we -- and because of
limitations with HEC-RAS on sediment transport functions, and that
sort of thing, we have a middle river model and we have a lower
river model in order to make that change because you can only
identify it single sediment transport relationship for both of them.
So I have to say I agree with you, that the system really is
much more of the supply limited system in the middle river and a
transport system in the lower river.
MR. VASQUEZ: Mr. Jose Vasquez, from NHC. It was not
clear from reading the ISR exactly how you're going to model the
tributaries. I'm talking about the middle -- just the middle reach,
okay, because I think that's probably the most critical in terms of
degradation, if it happens, it would probably be in that area.
And because in part when I'm reading, looks like you were
going to compute sediment rating curves for pre-project and then put
that as inputs in the model, and my concern with that approach would
be this: The way I picture it, I might be wrong, but after the dam, the
water levels in the summer would be lower. It means that at the
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mouth of the tributaries, it's going to over seep and that might cause
the tributaries to look a little (indiscernible) and supply more
sediment during that period. Sometimes (indiscernible).
On top of that might be the effect that we saw before of the
glaciers, if I understand some of -- I don't know if those basins are
glaciated but if there are changes, there could be also changes in the
sediment supply.
And so the point that I'm trying to make is the post-project
rating curves of the tributary may be different than pre-project.
Maybe a better way to model the tributary would actually be to
include them as actually branches coming into the main stem. Is that
possible or probably -- to do in the model?
MR. ZEVENBERGEN: I won't say it's not possible. The
tributaries in the middle river are contributing a pretty small amount
of water and sediment. And so they are treated as point sources and
with rating curves that we're developing.
And so relative to the supply from the tributaries, we
are -- what we're seeing, anyway, is that they're supplying virtually
no sand, and the gravels that they're supplying are considerable. But
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the evidence of fans throughout the middle river, you know, supports
the fact that they are supporting, providing large amounts of gravel.
I don't think that incorporating these small tributaries as actual
tributary reaches would be superior due to the fact that there's, again,
a lot of uncertainty inherent in any kind of an estimate on the
tributary sediment loading, and that that approach would only be a
very minor effect on the -- relative to that huge uncertainty.
MR. VASQUEZ: Okay. Yes. The reason for my question, of
course, we -- we understand in that experience, when one river
(indiscernible) be completely transferable to other rivers, we
understand that.
But there is -- there is the Peace River in Canada that was --
there is a big dam that was built many years ago. And what's
happened there is that there's been a lot of development of
(indiscernible) water surface profile because of sediment supply by
the tributaries that now, because the flows have been reduced, the
river is not able any more to move it, and actually had a big impact in
the morphology there.
I'm not trying to say that the same thing is going to happen
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here because, really, I don't know, but it might. That's what is
my -- the concern they're raising is actually because of that,
something like that may happen.
And yes, your point is actually good. You say that there is a
small amount of sediment coming from that, but if it's mostly gravel,
actually that's the most important, because that is the one that is
going to affect the morphology.
MR. FULLERTON: Well, we are -- we are doing
modeling -- sorry. This is Bill again.
We are looking -- investigating actually the interface or the
fans for many of the deltas or the tributaries. They're incorporated in
a number of the 2D models and the focus areas, some of the -- some
of the larger tributaries, Indian River, Portage, fall within -- in the
focus area. So there will be a modeling of the actual fan area within
that 2D modeling.
Then most of the tributaries, the ones that we identify that had
fans, we're going to look at the potential for accumulation or
extension of those fans into the -- into the middle river based on the
volume of sediment being transported, reduced ability of the main
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stem to transport, looking at how potential for constriction of the
river to adjust to hydraulics to be able to transport those fans away.
So that -- we are looking at exactly that.
Now, I think in terms of the degradation going up the
tributaries like -- I mean, when they're -- they actually get away from
the fans, they're pretty -- they're pretty controlled. They're pretty
coarse. They're pretty armored and I don't envision that that would
be a mechanism or concern. So the deposits where -- it's the fan
deposits that maybe you could cut through in some cases. And even
those are pretty course. I think it may be the opposite issue, not
cutting but the accumulation that is probably more likely.
MR. MCLEAN: Since we're talking about tributaries, I wasn't
quite clear, in the reservoir itself, you are not modeling any -- any
tributaries; is that correct? You're not doing a morphodynamic
model of tributaries coming into the reservoir? You're using other
methods -- you're using other methods to assess the geomorphic
changes on those tributaries in response to the reservoir levels?
Could you explain why you don't model that? I'm curious.
MR. ZEVENBERGEN: The modeling in the -- starts at the
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dam and goes on downstream, and then the focus areas are separate
models.
The models of -- we do have models that will look at the
sediment development from the tributaries in the reservoir, with the
surveys up there. We're not doing morphodynamic models of those.
We're treating those mainly as looking at sediment inputs, and then
also potential for areas along the reservoir perimeter.
MR. PHILLIPS: Guy Phillips. So, I'd like to check and make
sure I'm understanding what you're saying. (Indiscernible - over-
modulating) reservoir and aggregate ability, modeling changes in the
sediment transport and accumulation of the (indiscernible) reservoir
without (indiscernible - distance from microphone). With changes
that we can foresee occurring without the (indiscernible - distance
from microphone) climate changes or changes in glacier and things
of that nature in order to have -- without project (indiscernible -
distance from microphone).
MR. FULLERTON: So I guess to the -- and that -- currently,
we don't have that in our study plan, to be modeling with a different
climate scenario.
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But hypothetically, if you provide different hydrologic input,
we -- in terms of at least -- one of the drivers of the transport of
volume and the water and the discharge amount, we can incorporate
that because we're developing rating curves for the tribs that would
be related to the flow in the tribs.
So if we change that flow, that would be reflected in the
amount of sediment yield from those tributaries.
MR. ZEVENBERGEN: Are there particular tributaries that
you're thinking of related to that question?
MR. PHILLIPS: Not specifically. But we heard about the
changes in the glaciers, certainly a climate change topic which had
been discussed (indiscernible - distance from microphone).
MR. ZEVENBERGEN: So, your question related to
glacier-affected tributaries then.
MS. GLASS: So okay back to my question that I asked Bill
that Lyle I've been waiting for you to answer because Bill said you
would.
And I think I know the answer after listening to you, but can
you explain again why you stopped the modeling at Susitna Station
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and did not go all the way down to the Inlet?
MR. ZEVENBERGEN: Thank you. And actually, the -- the
initial models that I've been showing and -- okay, I'm hitting the right
buttons now. You know, this part of the presentation was to just
describe a little bit about these initial models, some calibration.
So this slide shows some of the hydraulic calibrations, some
comparison of observed versus model, hydrographs and stage
hydrographs at the various gages. A decent hydraulic calibration,
decent sediment results in terms of the observed versus how the
model is comparing in terms of sediment loads.
The domination of the sediment loads by sand, but the fact that
there are gravels in transport, and that we are in these initial models
doing a pretty good job of capturing not only the transported loads,
but also the transported gradations throughout the models.
So that was just to say, yes, we are going to make this decision
as to whether to extend the modeling, fluvial geomorphology
modeling below 29.9. That decision is based on these models.
So this is all from the existing-conditions model. You know,
the green dots on this are 9,000 sediment transport results, daily
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sediment transport results over a 50-year simulation period.
The large dots, you know, are over several years with the
USGS measurements, but the green dots are from the simulation
results.
So, in terms of the decision to extend fluvial geomorphology
modeling below 29.9, in the ISR we indicated how we would make
that decision. Basically it would be looking at what is the project
effect at 29.9, or in the vicinity of 29.9, projecting that downstream
of 29.9 and saying, you know, what can we -- what can we learn or
what can we surmise about the potential effects downstream of 29.9
from the model that we’ve done.
And so we looked at basically three things -- or four things,
and they're all to the extent possible, based on how much change
would the project have at 29.9 and below compared to natural
variability. If you have a very large range of natural variability and
then a tiny project effect, then there's no need, no value in extending
the modeling below that point.
And so we looked at flow, so the hydrology. We looked at
how that could affect channel form both in terms of channel width,
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you know, is the channel going to widen, is it going to narrow;
looking at bed aggradation or degradation; how will the channel
change vertically; the sediment transport volumes with and without
project, and when I say with "project," I'm talking about the one
scenario that we have looked at in more depth and that's the OS1b
scenario.
And so sediment-transport volumes, sediment-transport flow
depths and velocities in terms to the hydraulics. All of those factors
play into, you know, how much change, how much effect could be
below 29.9. But our gauge really is the range and variability of the
natural system.
And this is very light in terms of if you read the technical
memorandum, you'll see a lot more detail, and I really invite you to
read that technical memorandum to see, you know, how we made our
decisions.
On the left side here, we have the flow duration curves and this
is for the open water flow season. So we're looking predominantly at
our -- when the sediment transport is occurring, and that's during the
open water flow season, and looking at how does the flow change.
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So the blue lines on there are annual flow duration curves
during -- basically from May through October. We always started at
the beginning of the open water flow season, so sometimes that
would go into April, and then the end of the open water flow season,
and we got that through the ice processes study when -- you know,
when the river became ice dominated looking at Talkeetna.
So the blue lines show the range of flow duration curves on an
annual basis. The green lines show the flow duration curves for that
same 50 years with OS1b operations.
Now, you see that there is a tendency to shift the flow duration
curves down, meaning lower flow during the open water flow
season, but almost entirely within the range of natural variability.
There are -- if you look at the far left of the curve, there's a 10,000
CSF -- let's see, it's not 10,000. It's 50,000 CFS is the first line,
100,000 CFS is the second line.
Right where the second line crosses there, you see a couple of
curves that fall a little bit below, the green lines fall a little bit below
the blue. So, those are the only points in time during the open water
flow season that the operational condition would be outside the
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natural range of variability for the existing conditions.
The reason for that is that it's dominated by the Chulitna,
Talkeetna, and Yentna flow because they're the predominant flow
sources. So, by the time you get here, the operational effects are
small in relation to the natural variability.
It's not shown here, but in the technical memorandum, it would
be (indiscernible) monthly flow duration curves so you can say June
is the month that I care about, July is the month that I care about. So
you see the flow duration curves for those individual months, and
you can see how much that those are affected.
Again, with those, there's a large range of natural variability
and a relatively small change.
Width variability, we -- based on the new hydrology that
would be occurring during operations, we anticipate that the channel
will narrow through the middle river and below. Below 29.9, we
anticipate approximately 5 to 6 percent chance of long-term channel
narrowing. How rapidly that will occur is debatable.
I personally think it will occur over decades, but the right slide
shows how variable width is now with the blue dots, and a 6 percent
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change is shown in the red line versus a thin trend line that's going
through that data. So, large range of natural variability, small change
related to the project.
I'm going too long, aren't I?
MR PADULA: You want to make sure Dara gets her question
answered.
MR. ZEVENBERGEN: The other part of that decision looked
at sediment loads. This is annual sediment loads with and without
project.
The dark blue line is with project is existing. The white
[hatched] lines are with project so sediment loads are going to
decrease.
While we're trapping sediment in the reservoir we're also
affecting the hydrology. So this modeling incorporates both of those
things and shows that we are definitely reducing sediment loads
within a large range of natural variability.
One question would be are we going to change the substrate?
And so, again, that's -- substrate that you have below 29.9 is
dominated by the Yentna. The Yentna is not going to change. It's
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going to still put in a whole lot of sand.
It's also dominated by the Chulitna, which puts in more gravel,
but a lot of that gravel does not get past 29.9. It doesn't now and it
won't with the project. So that gravel is accumulating in the middle
river -- in the lower river, sorry. That would be pretty hard for it to
(indiscernible) the middle river.
MR. ZEVENBERGEN: So, in terms of -- and this is
something that I don't have a graph for and I actually haven't
produced a graph yet, but the model will be able to tell us, and I'm
sure that it'll say that the gradation of that supply is, you know, very
minorly affected and I would be surprised to see much, if any, impact
related to that. Maybe because it's dominated by the Yentna River.
The next thing would be the aggradation, degradation. Now, if
the river were in an equilibrium state today, it would tend to say that
we have little long-term aggradation or degradation. It was purely an
equilibrium of the sediment supply.
We don't have that in the lower river. We have a braided
system that is -- shows every sign of sediment accumulation through
that lower river, the multi-thread channels, the braids – braid plains.
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You can definitely see in any kind of aerial photograph where the
sediment is being accumulated.
And so this graph shows on the left the reach average in the
dark blue lines, aggradation under existing conditions, and then the
right side, the blue lines, reach average degradation for with project
conditions.
Basically the river stays aggradational, but only slightly less
aggradational, so the form of the channel, the character of the
channel would remain the same. The more variable line there looks
at sediment just volumetrically, sediment accumulation as you move
down the river through the lower river, so the -- down to 29.9. So
sediment loads, sediment transport capacity, similar character of the
river, that leaves us one other thing, and that's the hydraulics.
Looking at the wet, average, and dry years, this shows depth
on the left and velocity on the right. And you can see, there are
periods where velocities are low. The solid lines are existing and the
dashed lines are with project.
So again, we see a tendency for a little bit lower depth, a little
bit lower velocity for -- with project conditions. Not too surprising
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because we're reducing the amounts of flows. So we would expect
lower depths and lower velocities, but within the very large range of
natural variability as depicted by the red versus the green versus the
blue line for wet, average, or dry years, so we're showing the range
of conditions.
So in a nutshell, we concluded that there is a very large range
of natural variability with everything that we looked at, whether it's
velocity, flows, sediment transport, and the -- as the basis, as the
existing condition.
By the time you get to 29.9, you know, this will be a very
different conclusion in the middle river, but by the time you get to
29.9, all of the tributaries dominate the conditions that we see there.
We see minor change in every -- everything that we've looked at
compared to a large range of natural variability.
We also see that the channel form should be maintained into
the future in that aggradational system.
So, when we do go outside the range of natural variability, as
that second lowest bullet states, it's only by small excursions. So, in
terms of the processes, whether there's sediment -- and I think that
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would extend to fine sediments, to turbidity, all of these things. It's a
process of dilution. All of the tributary amounts are dominating
the change that's occurring with the project operations. So, very
small change, very large range of natural variability.
So why are we recommending not doing modeling below
29.9? It's because we don't see impact at 29.9, and the impacts below
29.9 should be less as you move further down, especially when you
get into the tidal zone. The tidal zone is going to be dominated by
the tides.
And the small operational change going into the system where
the tide range is the dominant feature creating the tidal currents,
creating depth morphology is, again, very, very minor.
So our decision, our recommendation is to not do any further
modeling in terms of computer modeling down below 29.9.
MS. McCRACKEN: This is Betsy McCracken with Fish and
Wildlife Service and I just have a few--
MR. PADULA: Sue, do you have any questions?
MS. MCCRACKEN: So I think you said you looked at the
open water period from May to October, and I'm wondering if we
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have information that addresses the increased sediment transport in
winter, and whether or not the project would alter the seasonality of
sediment transport?
MR. ZEVENBERGEN: We don't have modeling for winter.
That -- that extends -- well, in terms of the geomorphology model.
We do know that sediment transport in the middle river is pretty
much nil during the winter. The sediment supplies from upstream
are locked up into the ice and the production from upstream sources
is gone during the winter.
The -- as you move further down the system, the flow rates
are so low that we're in -- really into a negligible amount
of -- negligible amount of sediment loads in the -- you know, in those
ranges where the flows are in the thousands and 10,000 CFS, and
that is supported by all of the data that USGS collected. So nominal,
minimal sediment transport.
MS. MCCRACKEN: So does the project currently have a way
to -- or plans to address the winter conditions under the project, the
sediment transport?
MR. ZEVENBERGEN: The ice processes study is doing the
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ice-covered modeling throughout the middle river and it -- as part of
our interaction, we will be looking at the results of those models to
see if they could initiate sediment movement.
It's our suspicion that they won't, but that is part of what
we -- our interaction would be with them, is to look at their model
results, do their model results indicate that sediment could even --
any sediment movement could even be initiated.
In the lower river, again, the amount of flow is going to be
very low, and so the sediment transport, as you saw -- well, I think
you can see it in those graphs, just the amount of sediment transport
is towards the low-flow conditions, is negligible in terms of channel
form. Channel form is dominated by the higher open water flow
season.
MS. MCCRACKEN: So will the ice processes have also a
decision point related to this?
MR. ZEVENBERGEN: Not to my knowledge.
MS. MCCRACKEN: Okay.
MR. DYOK: I was going to say, let's have Jon Zufelt come
up and maybe respond to that question.
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MR. ZUFELT: So -- Jon Zufelt leading the ice processes
study.
And the ice processes model is only for the middle river. It's
only for the dam site down to approximately mile 100, the three
rivers area, and the main reason is because as you go further down
the river, as Lyle pointed out, we're in a very highly braided system,
highly variable system and that would be impossible to model ice
processes in a braided system like that.
MR. DYOK: So maybe, Jon, could you explain I think for
Betsy because her question is that you're anticipating that with the ice
condition, that you would have sediment movement down in that
reach below river mile 29.9. Is that your question, Betsy?
MS. MCCRACKEN: Well, I'm just trying to understand
where we're looking at the winter -- the increased sediment load
during winter under the project operations and where the decision is
coming from or not coming from as to whether we extend it to go
below project river mile 29.9.
MR. ZUFELT: So one of the things that we have done is that
the winter bed sampling -- and with the winter bed sampling,
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the -- you know, we were able to see clearly, you know, down to the
bed in most cases and we saw very little sediment transports and
sediment movement in those conditions, and that's why we -- you
know, why we did that through ice video, to look at the bed material
during that time.
So -- but the relationship to channel morphology and, you
know, channel change is dominated by high flows, peak flows,
extreme flows. And so the range of flows during the winter all fall
into almost a non-sediment-transport condition, and I think that
would be the case both with project and without project, and you
know, so that in terms of a channel morphology or any kind of a
decision related to that, the project range of flows is almost outside
of our ability to -- well, of our need to look at, because it would be
such a minor amount of change.
MR. PADULA: Thanks, Jon. I see some hands over here.
MS. GLASS: I have a question is not related to the lower
river. You had a slide that was alluded to being an amount of area
that you wanted to reduce (indiscernible) and looking at those areas
or something like that. My concern with that or at least at home why
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my people are considering this is that the HEC-RAS1 model isn't
nearly as powerful as the other one. And the second model provides
a whole lot more information on things like (indiscernible) patterns
and they have direct impacts on our ability to evaluate ground water,
subsurface flows (indiscernible) in spawning areas and instream
flow, habitat conditions post project. So, the more that HEC2 RAS,
HEC-RAS modeling is limited and directly limits our ability to
address the groundwater issues and fish habitat issues. You know, a
smaller area we're modeling with this and smaller area we can do
with the rest of it. So I was just hoping that, you know, there's --
within team discussion about, you know, how much you want to
limit in doing your modeling.
MR. ZEVENBERGEN: Yeah. And this is -- this is the slide that
you're referring to that has the future decision point as to the amount of
2D modeling that would occur in the focus areas and I agree that the focus
area models, the 2D models are a really important tool for us to evaluate
all the conditions that you were describing.
The reason that we have this decision point in there is that the
2D modeling is a large amount of effort, it's a large amount of money
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and we wanted to at least have it out there that if and only if, we see
that this operational scenario gets us virtually identical results to
another operational scenario, that we don't need to continue doing
both of those operational scenarios at every focus area or, you know,
it really -- you know, when we see a limiting -- limitation on the
value of all the extra effort, if it's just going to be the same as the
previous model, the same as the two previous models, for finding the
same conclusions at every single focus area that we move through,
that we would say -- well, we can step back and say we're not getting
any additional value for that.
So the 1D model, you know, is -- does provide input to the 2D
models. So if two different scenarios produce, you know, nearly the
same result as the 1D model, then it's not feeding different
information into that focus area.
Or if there -- the change all occurs in 25 years, do we need to
run 50-year models for each situation. You know, that's the sort of
thing that we're going to look at.
And so it wouldn't be done in a vacuum. It would be done,
you know, in -- working with the other study areas with consultation
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with AEA, and then, you know, as we have future TWG meetings, I
understand that we want to have future TWG meetings and so, you
know, we're going to be working through the multiple focus area
models, and we'll start providing those results and what we're seeing.
And so it will be an informed decision.
MR. FULLERTON: Yeah. We put in there to get it out there,
that idea out there in front. And part of it was in response -- I mean,
when we did the POC, a number of agency folks said well, that is a
lot of info, how are we ever going to look at all that information for
all those scenarios, for all those focus areas, for all those flows. And
you know, if they can decide that there are certain parameters or
metrics that we look at more with that -- that -- you know, a more
limited set of focus areas addressed that are important for what is
happening with that scenario too, then it's a consideration, it's not
something that we're saying, you know, forcing, but it's something
for us all to consider to maybe make all our lives a little easier so we
can focus in on what's important and not be overwhelmed by -- some
modeling results that might be fairly similar across scenarios or focus
areas.
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And so we don't know if that's happening or not, but if just, in
fact, if that's how things start developing, maybe we should have that
as these discussions.
MS. LANCE: Ellen Lance, Fish & Wildlife Service.
I find myself reflecting back on Guy Phillips' comment earlier
about looking at the effects of climate change on the system, and I
find myself not being able to be convinced that dropping the lower
river is wise at this point without considering the full effects of future
conditions.
MR. ZEVENBERGEN: We're not dropping the lower river.
We're not extending further. But so is your concern that we're going
to drop the lower river?
MS. LANCE: Well, what I guess what I heard you say was
that the baseline conditions, the variance in baseline conditions
far -- basically swamps the signal that you're getting from the project
effects.
But I'm not convinced that you've actually looked at the full
suite of possibilities for future conditions if you haven't considered
the effects of climate change.
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MR. ZEVENBERGEN: I would -- I would think that any kind
of climate change would only tend to increase the variability. But
remember, we're always looking at a comparison of existing
conditions to -- with the project, so that if we said that climate
change was going to increase flow, we'd then need to increase flow
for existing -- you know, for our existing conditions runs as well as
the [US1D].
And again, the project would be a small change once you
consider Chulitna, Talkeetna, and Yentna Rivers. So, I think that it
would be an equal comparison, would be my suspicion, just in terms
of how we are always making the comparisons.
MS. LANCE: It would be good to see that to be convinced.
Because I think the other -- the other rivers will change as well. The
other rivers that you named; the Yentna, for example, to see how that
(indiscernible), you know, the different flows might impact below
29.9.
MS. WALKER: Is it my turn? This is Sue Walker with
NMFS again.
And in listening to this presentation, which is very interesting,
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the questions that arise are how is the glacial change in hydrology
study feeding into this study. Is there a link?
MR. ZEVENBERGEN: No.
MS. WALKER: It does seem as if there should be a link when
this 7.7 is addressing the input in changes in hydrology into the
reservoir and the river.
And also, does this study feed into Study 9.12, --
MR. ZEVENBERGEN: The barriers?
MS. WALKER: -- the assessment on fish-passage barriers,
especially tributaries coming into the reservoir? Will sediment
deposition affect fish migration into and out of tribs and the main
stem above the reservoir?
MR. ZEVENBERGEN: Yes.
MS. WALKER: As far as sediment transport in winter, we're
looking at a change in the middle river of roughly a 1,000 CFS flow
right now, fairly steady under ice, to between 5 to 7,000 peaking up
to 14,000 in load following manner.
How does this increased winter flow affect sediment transport,
at least in the middle river? I think what I'm hearing you say, and in
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looking at your graph, you logarithmic graph, but that is still too low
of a flow to induce sediment transport.
MR. ZEVENBERGEN: It is.
MR. FULLERTON: Yes, but also the other thing to remember
is that the middle river is predominantly from what we've seen and
what we've seen both in the modeling and in the -- or observations as
supply limited condition. So the bed -- in terms of bed interaction,
even during the open water flow season there's very little bed
interaction that we're seeing.
So in the winter it --
MS. WALKER: Even during high flow events?
MR. FULLERTON: Even during high flow events.
MS. WALKER: In summer?
MR. FULLERTON: In summer.
MS. WALKER: Okay. How does the increase in daily
variable flow in winter affect ice? And I know ice is kind of a
significant impact on channel formation and maintenance. Will the
ice model be able to predict how jams are formed and blow out and
backwater and how those will affect, those processes will affect
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sediment transport?
MR. FULLERTON: Jon, is that a yes?
MR. PADULA: I think you're going to have to ask Jon Zufelt.
First thing tomorrow Jon is up with his presentation.
MR. PADULA: Go ahead. What was that comment?
MR. KONIGSBERG: This is Jan. Can you hear me?
MR. PADULA: Yes, Jan, I can hear you today.
MR. KONIGSBERG: (Indiscernible - interference with
speaker-phone.) I’m hearing myself echo. Assuming there is no need
to study the Lower River, from the standpoint of sediment transfer
and morphological change of the channel because of the
tide…(indiscernible)…I guess my question has to do with, and I’m
not trying to jump ahead of the ice modeling, but the ice processes
(indiscernible) ice model (indiscernible) in the ISR. But going back
to the channel changes, the morphological change (indiscernible) ice
cover (indiscernible - over-modulating.) without considering
(indiscernible).
MR. ZEVENBERGEN: Yes, from an observational
standpoint, and I think Jon, I'm hoping you will agree with this, and
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if you don't agree, please say so, but we're not seeing strong ice
effects in the lower river under existing conditions in terms of
channel morphology.
We do see strong ice effects and fluvial effects in the middle
river. But in the lower river, it's not -- doesn't appear to be an
ice-dominated condition.
MR. KONISBERG: I just want to follow up and say that
you’re not seeing ice effects in the lower river affecting vegetative
cover.
MR. ZEVENBERGEN: Ice effects on vegetative cover in the
lower river might be a good question for Kevin, but I think that
the -- I think that the vegetation and the forms of the river are not
dominated by ice in the lower river, would be my presumption.
MR. PADULA: So, Jan, again tomorrow we cover ice as well
as the riparian studies, so combination of that information, and
hopefully you will be with us and we will get to that question
tomorrow.
MR. FULLERTON: And I want to clarify something and, you
know, in terms of decision point, that decision point was not to not
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model the lower river with our 1D model. The decision point was to
not extend the model any further down in the lower river than we
already have, which is down to Susitna Station, which is at roughly
mile 30, and we're modeling 70 percent of the lower river.
So it's going to the point where we're below where the Yentna
contributes its water and sediment supply. That's where we're
recommending that we stop the model, the 1D bed evolution model.
MR. PHILLIPS: Guy Phillips, Kier Associates.
Another check-in question that has several parts depending on
the answer to the first one. I understood you to say, while I fully
appreciate that your focus is downstream on the dam. I understood
you to say that you would expect to see sediment accumulating
behind the dam. Is that correct?
MR. ZEVENBERGEN: There is going to be sediment trapped
by the dam, yes.
MR. PHILLIPS: Yes. And so is there, either by you or
anyone else, work on the way that will evaluate the quantity,
location, and character of those sediments being accumulated on the
dam?
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MR. ZEVENBERGEN: Quantity location and caliber, I think
yes.
MR. PHILLIPS: Yes, someone is doing that?
MR. ZEVENBERGEN: That's us. It's being done in the water
quality model study with two -- the reservoir model.
MR. PHILLIPS: Okay. So if in the power side of the analysis
of this project it becomes clear that sediment flushing will be needed
to clear the reservoir for power production purposes, will you be able
to evaluate the impact of that downstream?
MR. ZEVENBERGEN: As a hypothetical, if flushing were
needed, then yeah, we'd be able to track that sediment through the
system.
MR. PHILLIPS: Okay.
MR. MCLEAN: This is Dave McLean. The question of the
reservoir is so puzzling, I guess. Of course, it's a huge reservoir
compared to the volume of sediment coming in, so we're not talking
of it filling it in 20 years.
But in terms of changes to physical habitat, questions of where
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gravel would accumulate, delta formation, those are not really water
quality problems, in my view. They would be geomorphic questions.
And so I was a bit concerned to hear that it's simply coming
out of a water quality analysis. Surely the -- the -- I mean, this is
where models have tended to be used successfully. We have a better
track record of running HEC-RAS models in reservoirs than we do of
using them to predict downstream impacts.
So I guess I'm really surprised that you're not making an effort
to use those kinds of tools, both for individual tributaries, if they're
important for fish usage, and just even to figure out the footprint of
the reservoir. Because over decades, there will be a fluctuating
backwater region that will extend upstream, so your footprint
actually increases over time, which has certainly become an issue on
some reservoirs we've worked on on the Columbia River.
MR. ZEVENBERGEN: Well, the water quality model, the
[EFDH], the vast majority of the sediment loading in the reservoir is
the finer sediments and it has much better capabilities to model the
fine sediment than RAS does.
MR. MCLEAN: Well, of course. But what we're talking
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about is the gravel will deposit at the head of the reservoir and cause
a fluctuating backwater region that will -- or delta formation, which
will be -- consist of coarse sediment. There'll be a – sediment will
sort, there will be a sorting process through the reservoir with the
fines, the silty clay deposited, and of course -- so I'm not really -- you
know, if it's not a trap efficiency problem in terms of reservoir life,
that may not be important to some people, or most people.
But the question of the delta formation and the physical
changes to the substrate, the effect that there will be a fluctuating
backwater region that will move upstream, those are not fine
sediment problems. Those are gravel bed load questions, or bed
material load questions.
MR. ZEVENBERGEN: And I think John is -- water quality is
next? And you can talk about the reservoir model, because I think it
has more capabilities than you’re thinking here. It is -- EFCD model
is pretty robust especially when it comes to depositing the sediment.
MR. MCLEAN: So will there be boundary conditions on -- of
gravel input at each tributary to go into that model?
MR. ZEVENBERGEN: Not now. Currently you're not
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proposing to model the tributaries in that form. The main stem input
would be there, but right now it's not. It's finding a resolution that
the tributaries would be modeled with the EFDC.
MR. PADULA: So let's come back on -- just on the questions
relative to the water quality and modeling. We do have John
Hamrick this afternoon and it will be appropriate then.
MR. MCLEAN: Okay, the second question is during the
discussion, a comment was made, I think by Lyle, that said 5 to
6 percent chance of narrowing in the middle reach. I assume you
meant the narrowing -- the river is going to narrow by 5 to 6 percent,
is your prediction, right?
MR. ZEVENBERGEN: Yeah. I'm sorry. I must have
misspoke, yes.
MR. MCLEAN: : And that kind of prediction is not really a
modeling -- presumably the numerical models give you no
information of any great merit to predict width changes. Very few
modelers have claimed they can predict bank erosion rates,
encroachment rates. Those are more processes governed by
vegetation establishment, perhaps ice formational changes. So this is
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a non-modeling prediction, I assume?
MR. ZEVENBERGEN: Yes, it's based on hydraulic geometry
relationships and the changing flow.
MR. MCLEAN: So you just take Q.5 power and come up
with --
MR. ZEVENBERGEN: Yeah.
MS. MCLEAN: That's about -- so that's a
back-of-the-envelope sort of --
MR. ZEVENBERGEN: That's what we said we would do in
the ISR, and so that's been -- that was -- you know, we said that's
how we would do it, and that's what we did.
Now, I'm not going to suggest that I -- that my models can
predict bank erosion or -- or accretion, but in the lower river there is
plenty of sediment for accretion to take place, especially, you know,
with the aid of vegetation that would also encroach into the areas
because of the changing hydrology.
So I think it would occur. You know, I'm not saying that
5 percent is some perfect number or anything, but you know, I think
it would occur and I think it would occur in matters of, you know,
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decades to the, you know, 50 years would be a reasonable amount of
time for that to occur.
MR. MCLEAN: So that kind of prediction would come out of
your succession analysis that you briefly mentioned at the beginning.
You talked about how you've characterized channel changes over
time as a floodplain formation and vegetation.
So this kind of information, it may be able to improve the
predictive ability rather than just relying on regime equations, or is
there other ways you can look at this? I mean, the regime approach
seems -- like I say, it's -- I mean, we can all do that in about ten
minutes.
MR. ZEVENBERGEN: Yeah, I think that's about how long it
took me too.
But it is the -- it's a solid way of making a long-term prediction
on channel form. There's -- Julien did it on a reservoir in -- I think it
was in Vietnam, but the -- you know, in terms of looking at the
change in hydrology, the change in -- predicted change in channel
width and the actual change in channel width over time.
And I do want to point out that in the lower river where we
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have sediment, we expect accretion combined with vegetation. In the
middle river where we would not have sediment, we would expect it
to be primarily from a vegetation encroachment with -- I mean, no
available sediment for actual accretions (indiscernible) much more of
a vegetation colonization in the middle river.
MR. MCLEAN: So this -- this might be one of these instances
where case histories from other rivers of somewhat similar form
would be worth reviewing, and so far there's a very large body of
literature on the Nechako River, there's also -- on the piece that might
help you.
Because essentially, the narrowing on those rivers was
essentially a vegetation process, and -- but there's a lot of room for
feedback of other processes in your physical setting. You've also
got changes in ice. I mean, it would be very worthwhile, I think, to
look at that kind of thing.
MR. ZEVENBERGEN: And we agree.
MR. PADULA: Thank you. We have one in the back. Mike?
MR. HARVEY: Just sort of to come full circle on that one the
issue of the literature review. You know (indiscernible) to review
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does incorporate that, does look at the stuff in the (indiscernible), it
does (indiscernible) basis for what Lyle sort of finally decided that
there is no really deterministic way of predicting this (indiscernible -
distance from microphone).
You can't -- past performance on the Susitna does not give you
that information because we don't have (indiscernible - distance from
microphone), do not have that situation.
We do know that channel --
MR. MCLEAN: But you may have -- but you may have
long-term patterns of changes in runoff over decades that you may be
somewhat indicative, so you could look at -- you can relate long-term
trends in hydrology and run-off patterns to changes in channel
geometry or channel pattern in an attempt to look at those kinds of
(indiscernible) [changes].
MR. HARVEY: I don't think this system is not sensitive
enough to do that. I think you'll find the middle river is extremely
insensitive. I think everything we found out about it to date would
suggest that. The lower river might be different.
But I think the use of a hydrology geometry relationship is not
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wrong. There is a theoretical basis behind hydraulic geometry and I
think there's a lot of history of people using hydraulic geometry.
MR. MCLEAN: That's true. And first as they learn more,
they also recognize that those comparable relationships are reflecting
processes like, for example, vegetation encroachment and other
processes, bank stability, log-jam formation that stabilizes banks.
And so as we get more and more into having to answer complex
questions like this, I think you have to look at those actual drivers,
not just the empirical relation.
MR. PADULA: Thanks. Mike.
MR. WOOD: All right. This is Mike Wood. I’ll restrain
myself from going to the ice process – I’ll wait for Jon, however I do
want to just mention that both freeze-up and break-up is quite a
sediment transport event.
I also want to ask if you feel confident given 2013's huge high-
water events and whatnot, that you collected enough data. I mean, it
was very eventful data for that model that we're seeing now. It was a
pretty significant year, 2013.
Yeah, I won't talk about ice too much, and I won't go down
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river below the three rivers, either. I'll keep it to the middle, what
you’re calling the middle river and I -- I want to understand that the
sand -- that river carries 90 percent sand and silt throughout the
summer months or that's what I'm hearing, and so during operations,
once operations begin, that sand and silt will be held back behind the
dam site meaning that the river will be flowing very well and clear
throughout the summer.
I take issue with someone saying that the water that would be
released during operations throughout the winter may have
significant -- insignificant effects on transport below the dam site
because of the amount of water you're planning to release. I believe
it will start picking up what is below the dam site and carrying it --
given the amount that they're talking about releasing.
And again, this has impact on the ice as well. As I said, I'll
restrain myself from that, but the sand and silt that is coming down
from above the dam is what we see all year long. I'm sorry, all
summer long beginning with break-up until about a week to two
weeks ago and now it's clear, we're getting it almost clear as you get.
Without that, if you increase those flows, I think especially in that
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middle river area where that's the greatest amount of impacts,
looking at fish and whatnot, those loads that you're talking about in
the winter and the amount of transport that could be happening
beyond then is very significant.
And like I said, I'll restrain myself on the ice process because I
believe that the shoulder seasons and the winter have a lot to do with
the geomorphology or whatever of this river, probably more
significant than the flooding events that we saw during 2013. With
that being said, I'll shut up.
MR. PADULA: Any response?
MR. ZEVENBERGEN: Yeah. I would just like to clarify that
when it comes to sediment transport, you need the ability to move the
sediment, and that's really strongly related to velocity. And you also
have to have a supply of sediment. The supply could be from the
bed, it could be from an upstream source, from bank erosion, that
sort of thing.
So in the summer when there is a supply of the sand and the
silt, it is -- you know, it's totally dominated in terms of the quantity
of sediment moving. It's dominated by that supply from upstream
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from the glaciers.
In the winter, the velocities are going to be very low and
they're not going to be able to mobilize the bed. Even the summer
flows can't mobilize the bed. So without a source of sediment with
operations, they'll just be flows that don't have a source of sediment
and don't have the capability, in terms of velocity, to pick up
sediment from the bed, other than, you know, the small amounts that
are, you know, stored here and there, but those are very small
volumes of sediment.
So, you know, I know that we increasing flows, but that
doesn't mean that there are sources of sediment that correspond to
those flows.
MR. WOOD: So when we see these flow rates, they
are -- they're carrying sediment with them and that's because it's
coming from above the dam site, right?
MR. ZEVENBERGEN: Yes.
MR. WOOD: You take those out, and you still have those
high flows. Isn't that water still capable of carrying sediment?
MR. ZEVENBERGEN: It's capable of carrying sediment, but
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there's no source for -- there's a limited source for that sediment.
MR. WOOD: Would that sediment that exists now in the river
as it is now pre-operation, not be picked up by the increased volume
below the dam site therefore creating the channelization of -- that
we're talking about?
MR. ZEVENBERGEN: And that -- you know, that is a very
common response to a dam in an alluvial system that has
transportable bed material.
What we're finding is that the middle river is so coarse that it's
not mobilized -- the bed is not mobilized for open water conditions,
and so it's pretty much a locked-up system to the coarseness of the
bed, so that what you're seeing in terms of sediment transport in the
middle river is purely supplied from upstream and it's carried
through. It's just a conveyor for that. You cut off the supply and
now you just have the water without the supply and it just moves
through.
And in terms of gravel, the amounts are very small, 99 percent
sand, 1 percent gravel. So -- and really, it appears that virtually all of
it is sourced from -- from upstream.
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MR. VASQUEZ: Jose Vasquez, NHC.
This question relates to the models that have been selected
from the 1D model and the 2D model. And as you mentioned, these
are better versions, the new releases -- actually, they haven't been
released to the public so you are the first that are using this model.
Nobody else, or a very limited amount of people, has used them.
And usually, you probably know by experience that it takes
several years for a sediment transfer model to actually be well tested
and start gaining confidence that it provides good results, because in
the beginning, they are very buggy and has a lot of issues.
In the case of HEC-RAS, maybe it has a longer history been
around, this is a new release, but you know, but in the case of the 2D
model, I would be really surprised that -- for example, you can
handle armoring well.
And just my experience using models, it takes a lot of time to
correct many of the issues that are --
So the point I'm trying to make is in order to be confident that
those models actually provide reliable results, validation is going to
be critical, very important.
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And I'm wondering how – especially for a process like
armoring, I think it's very important, it’s really complex. What are
the ways? I don't know if you remember when in the POC meeting,
we discussed, for example, like an idea, maybe a start with
subsurface (indiscernible) and run the model for existing conditions
and see the armor layer (indiscernible) or maybe there are other ways
to do it.
So I would like to know what are the strategies, what are you
thinking about how to actually validate this model correctly.
MR. ZEVENBERGEN: The validation process, I do want to
say that we do use those techniques of running with the substrate or
sub -- you know, the (indiscernible), having built the surface layer.
We might run the model for 15 years of simulation time to establish
that. That becomes our initial condition for the remaining runs that
we have.
So, you know, we employ a lot of the processes that you're
talking about and they've worked very well for us.
In terms of the armoring process, we actually have been using
the 2D model from the sediment transport standpoint for some time.
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This isn't the first time we've used the sediment transport model, the
two-dimensional sediment transport model.
And so we have a lot of experience with that model, what its
limitations are, the problems it has. And it does do a good job at the
armoring process from what we've been able to ascertain.
Now, again, with that model, we look at running it for a period
of time to establish armor layers and sort of thing and the results are
looking very comparable to what we're seeing in the channel.
And then to go back to -- I think that the winter bed sampling
was extremely valuable information because it did point -- and, you
know, there was a comment that the Susitna River is something that
we know -- that very little is known about. And I think that we're
gaining a lot of knowledge through each year that we're working on
it.
And to see that the islands are -- the bar heads and islands are
maybe not representative of the bed as the winter bed material
showed, but it's a much coarser bed than what the bar heads are, is
further evidence that it is a throughput system. But these are
constructional features, but they're not constructional features from
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bed material. They're constructional features from supply, is what
you have to conclude based on what we're seeing in our data and
what we're seeing in our modeling.
MR. VASQUEZ: Just to point out, so actually you mention
this strong variability across the channel in gradation. And how are
you dealing with that the 1-D model just takes a cross-sectional
average? How do you deal with all this natural variability in grain
sizes?
MR. ZEVENBERGEN: Well, the 1D model is intended and it
is really best suited for looking over long reaches. And so there we
do start off with -- and right now, all of our models are initial
models. We have a lot more data, a lot more cross-sectional data, a
lot more work to go into the -- especially the middle river model.
But with it we do start off with the substrate gradation, let it
build the armor. We're using that information to see how the model
variability and that sort of thing compares.
So the -- you know, we have to really avoid trying to look at,
you know, any one point in this model and say this is what's
happening at this point, in terms of the 1D model. We really need to
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be looking at it from a reach basis.
MS. MCCRACKEN: This is Betsy McCracken with Fish &
Wildlife Service, and I have a couple of questions.
The Services have been interested in the evaluation of other
operational scenarios other than the OSB1 (sic), and so I'm just
wondering if you have done any modeling for that scenario? And
also if -- if you -- if the modeling efforts have done any channel
maintenance modeling for pre- and post-project.
MR. ZEVENBERGEN: So we've only looked at OS1B
currently. You know, we will be able to very quickly now run other
operational scenarios to see how they would change things.
I suspect, from what I've seen with OS1B, that we're not going
to see a huge difference in model results for other operational
scenarios.
We also have not at this point and I think that that's -- this is
something that's going to happen after we run the initial range of
operation scenarios that, again, might look at what the channel
maintenance kind of releases or something like that could be, but
that -- we're not anywhere close to having to find what they ought to
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be yet, let alone, you know, whether they're needed, what their
magnitudes or durations could be. But so that is obviously on our
plate, but not for quite a while.
MS. MCCRACKEN: Okay. Thank you. I just -- I bring that
up because as you know better than I know, those flows are
important in creating and maintaining fish habitat and complexity of
the habitat and so we're definitely interested in that.
MR. ZEVENBERGEN: Yeah. The thing that we're learning
is that the middle river and the lower river are very different and so
that putting in a big flow into the middle river may not have much of
an effect.
The middle river is very much a locked-up system from a
fluvial standpoint. And the lower river is definitely an aggrading,
alluvial channel. So you know, the things that we can look at, you
know, we might see very little impact in the middle river and
potentially minimal impact for a totally opposite reason in the lower
river. It's a fascinating system.
MR. MCLEAN: Just a little further question on the modeling,
the 2D model. So are you going to present applications of the model
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to other, you know, comparison or have you already done that. I
guess I just missed maybe some of that earlier presentation results.
But if you run the model on other river systems and compared
it to validate it, or compared it as a quantitative morphodynamic
model. I know you've done work as a hydrodynamics model, but the
morphodynamics is the part that's the most important for validation.
And I guess I wasn't sure what sediment transport equation is
in the 2D model.
MR. ZEVENBERGEN: The 2D model has been run on other
rivers in terms of both the hydraulics and the sediment transport, the
morphodynamics, so we run it on the -- is it the Platte River, the Rio
Grande and then the Snake River as well.
And so -- and the Snake River has got gravel and sand and that
sort of stuff. They're looking at island development and that sort of
thing. So that -- so our experience with the sediment transport model
is pretty extensive.
MR. MCLEAN: The model itself is how many years old?
The morphodynamic 2D model, how old is it?
MR. ZEVENBERGEN: Would be five, six, maybe longer.
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It's not publicly available, but it has been around for a number
of years.
UNIDENTIFIED MALE: Used by the Bureau of Rec.
MR. ZEVENBERGEN: Right, by the Bureau of Rec.
MR. MCLEAN: So what was the equation you're using on the
gravel bed?
MR. ZEVENBERGEN: On the gravel, that -- it's -- it actually
does both. It has a separate equation for suspended and -- for the
sand fraction and the gravel fraction, you know, suspended versus
bed load. And I don't recall. I'll have to get back to you on that. But
in terms of which equation.
MR. MCLEAN: So in the middle reach, what you described
was a very supply limited, coarse-gravel-bed channel, I guess paved,
probably in those kinds of rivers, channel structure or bed structures
become quite important like imbrication. I mean, those factors
for -- govern threshold motion, like a degree of imbrication. I mean,
no one has even -- other than knowing that it changes the initiation of
motion by a factor of two if you're calculating -- using a Shields
parameter, no one has programmed those kinds of issues into bed
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sorting or bed-material transport rates. I mean, it's a pretty difficult
thing to -- and of course, at those low transport rates, the sensitivity
of the transport is just incredible. You change the velocity 5 percent,
you can change the initiation of motion or you can change the
transport by ten times.
MR. ZEVENBERGEN: Yes. Size is really what dominates in
this river D50 in a bed of 100 millimeters. The flows really can't
move that hundred millimeter deep 50 size with or without
imbrication. You can calculate it. And if you had imbrication that
would only make it less likely to move.
But the -- one of the really telling things in terms of USGS
data, if you look at their report from 1985, they estimated 5,000 tons
of -- of gravel moved -- moved back here. 350,000 tons of gravel
were moved in that year at the Chulitna River. So gravel surprisingly
-- it's a gravel-bed river, cobble-bed river that isn't transporting any
gravel. 5,000 tons is a tiny amount of gravel being transported, with
Chulitna at 300,000 tons, those are the USGS estimates for that year
and they correspond with what we're seeing as well.
MR. MCLEAN: Well, sometimes rivers may not carry a huge
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gravel bed load, but at least on the -- based on, say, a bed load
sampling measurement. I mean, one of the issues is, of course, a
Helley-Smith sampler has got an opening of 75 millimeters. You've
got 100-millimeter D-50 sediment, so that's an issue.
But also on other rivers, we -- I mean, we find that the overall
flux of gravel might be small, but when you actually look at the
amount of gravel being exchanged through erosion of bars or islands,
can be quite appreciable. So -- and if your real issue is habitat
change and spawning gravels, even that small amount of load starts
to become really the focus of everyone's attention.
And the fact that 20 million tons of silt is shooting over the top
of it, nobody really cares if it all goes straight out to the ocean. But
it's dealing with that small but very important fraction that becomes
much of the issue that you're dealing with.
MR. ZEVENBERGEN: Well, yeah. Historically you look at
the bars, and they're very, very static. You look at the '80s and the
'50s aerial photography, there is change, but it's not the kind of
change you would see in a lot of other rivers. It's not -- the river
system, the location you’ll find doesn't change very much.
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But then we are doing the two-dimensional modeling in the
focus areas, so in a movement of gravels and that sort of thing within
the focus areas is something that we can look at and we are looking
at, so we are looking at those substrate changes.
MR. PADULA: Thanks, Lyle. I've got a couple of questions,
but this gentleman over here first.
MR. VAN DER VINNE: Gary Van Der Vinne, Northwest
Hydraulic Consultants.
You talked earlier on the modeling releases from ice jams in
the future. You haven't done that yet, I guess?
MR. ZEVENBERGEN: No.
MR. VAN DER VINNE: Are you confident that you are
going to get enough information from John to be able to do that?
MR. ZEVENBERGEN: Absolutely. You know, this has
probably not been done before, so we're going to have to look very
carefully at what information we have, both observational and from
the models that they're producing, and then based on that
information, we'll develop strategies for making those runs.
But yeah, it is new territory.
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MR. VAN DER VINNE: Yes, because the ice models don't
really predict formation and release of jams and that's what you're
looking for, is it?
MR. ZEVENBERGEN: Yes. And what we are planning on
doing is looking at what information we do have observationally and
from this model to set up a jam storage, release it, and to develop a
pulse that would be a pulse from -- you know, from a hydrodynamic
probably 1D model to then provide a discharge boundary to run
through the 2D model so that we wouldn't be simulating ice jam
formation or that sort of thing, but we would be simulating the
effects of a break-up jam releasing.
MR. VAN DER VINNE: Just thinking in advance and trying
to see what the effects are in that similar event, okay.
MR. ZEVENBERGEN: Yeah. And we have some data
from Gold Creek, if you look through the stage records and that sort
of thing. I mean, you do see situations where we get four foot of rise
over, you know, 45 minutes, you know, and that's because of a jam
that broke upstream and now it's pulsing through Gold Creek. So
you can see that kind of -- you know, we know it happens and it's
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nice to be able to see the effects of that just in a gauge record, for
instance.
MR. VAN DER VINNE: But do you have any sense yet of
how significant the sediment transport is during break-up relative to
the overall loads?
MR. ZEVENBERGEN: You know, I think that the -- from
what I've seen, the concentrations are going to be quite high, but
they're also very brief. So just from a kind of an effective discharge
analysis, they might not contribute, and I don't think they do
contribute, to the overall sediment transport, but in a certain location,
they can be very effective in terms of depositing sediments in the
over bank areas and causing erosion in those areas, as well.
MR. HARVEY: And if I can just sort of add to that. We have
actually been trying to measure what is happening depositionally
from the ice jam surges in the backwater at various -- of the focus
sites, so we're actually getting measurement of deposition primarily
of sand size material that was present in the bed of the channel at the
end of the last open water season. Sits there over winter, and then
becomes available for transport out of the bed through the break-up.
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MR. WOOD: This is Mike again. I just wanted to say I
finally agree with you on something; that the bed surface is
armor-plated and I think, the reason for that is to protect itself under
the ice for sure.
But I do want to ask, are you integrating David Brailey's
studies of his cross sections and what he's seeing in the movement of
that bed into your modeling? Because the statements you're making
would lead me to believe that you may not be.
And then I also just want to say on a personal note. I mean,
every acre and anything that I have ever put in that river to try to
hold something down disappears within days, gone downriver, and
it's not stationary whatsoever. So those were my two questions.
MR. ZEVENBERGEN: Well, we're using all of the data that
Dave Brailey has collected. So in terms of an anchor or something
like that moving, it doesn't surprise me, but the river is armor-plated.
There probably isn't really much for an anchor to grab on to, as well.
And, you know, it's projecting up in the flow and prone to that kind
of movement.
But in terms of bed mobilization, that's really what we're
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looking at. We're not looking at does an individual particle move,
but does the bed mobilize. And if it's armor-plated to protect itself
from ice, as you're, you know, suggesting, then it really can't
mobilize during open water flows.
MR. PADULA: Does anybody want to eat? I mean, I
appreciate the discussion and the questions, I think, are very good
and we'll come back to some of those elements in the afternoon
discussions. It is 12:30. I think everybody deserve an hour for
lunch.
So again, we'll start at 1:30, and then again we'll probably --
I'll anticipate we'll go beyond 4:30 for those who can stay with us.
(Off record.)
MR. PADULA: We're going to get ourselves going again. So,
on our agenda, 1:00 has magically become 1:30, but we'll keep the
same order. Harry will move us efficiently. We're at Baseline Water
Quality. All right, please speak into the microphone, please..
BASELINE WATER QUALITY (STUDY 5.5)
MR. GIBBONS: Okay, how's that? I broke it already.
So Study 5.5, Baseline Water Quality.
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We're going to go through the slides fairly quickly so we can
get to the discussion.
But the basic objective of the water quality study is to take
historical data along with data we're currently generating and pull
that together so we have an understanding of what's going on in
terms of water quality.
Also to help build a database for temperature and
meteorological information, so that that continues with the water
quality perimeters into the model so that -- with other models so we
have a comprehensive look at what's going on there.
So we're looking at not only a physical chemical and
biological characteristics of the system, but also looking at some
contaminants, potential contaminants, some metals and sediments
and the fish. Sorry about that.
And in the sediments themselves and the characteristics of the
sediments. That's for multiple reasons because we need to
understand not only the water flowing by but what's in the sediment
itself.
So, one of the things we did do also to help augment the
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temperature information and help with sizing certain samples from
many different studies is the thermal imaging. Now, we didn't
complete all of that. We'll get into that in more detail, but we got to
most of it.
So some of the variances that we had, we need to talk about is
one of the things we were ambitious about was setting out continuous
measurement flow of the thermistors across the river at several
different stations, but because of logistical problems in terms of aces
-- not necessarily access, but just physical characteristics in the river
and holding those thermistors in place, is the discussion earlier this
morning about an anchor not holding it in place. That's what we
were trying to do, was anchor them. So we successfully did 28
different sites starting in 2012 /13 and this year, of course.
Okay, we had a couple of sites of a water quality and main
water quality sites. We had 17 sites. Three of those sites we had to
move from the project river model as in the study plan slightly
because of just , again the logistics of getting in.
We also had a variance, a slight variance in terms of some of
the sites, two of the sites, and we had trouble with cross-sectional
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sampling like we had planned to do for both cross sections across the
river and at depths, there was only one representative site in that that
cross section of the samples.
The plan was to take ten sediment -- detailed sediment
samples. We took like four in 213 and completed six this year.
Groundwater, we sampled six piezometers. I have four focus
area sites on some of them.
Some of this, this is just a smattering of some of the data that's
in the ISR that was -- by the time of the ISR, we had to put it out
only part of our data was completely QA/QCed that's what's in the
ISR, and this represents some temperature, the weather station on the
right, meteorological information there is representative and
chlorophyll A.
So it shows a characteristic of some of the data that we have
there and we have more coming, so we'll see.
I'm going to go through -- there were some modifications.
The first modification in our thermistor readings, we were
taking thermistor readings every 15 minutes. We had proposed to
change that to 30 because of battery life, so we could have data
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storage to make sure we were able to repeat that data. We overcame
that problem and we left it at every 15 minutes. So that's really not a
modification. It was supposed to be but we didn't. A good thing.
We have installed a meteorological snow measurement so we get that
sensor in terms of water equivalent (indiscernible) meteorological
stations currently.
Other modifications, the main one was, as we went through
some of baseline water quality we found that there was some
analytical inconsistencies. I'm the old guy on the block so I'm
looking at does this data represent reality?
The same thing when I looked at the model. Is it representing
the real world. Some of our data didn't look quite right, even though
it passed some of the analytical procedures that they followed. Our
QAPP was very rigorous and demanded that we really look at it. So
there are some samples that we need to verify and take additional
information 2014 so that's part of the modifications. So most of the
metals except for calcium magnesium, total mercury, total
phosphorus, the nutrients and Kjeldhal nitrate (indiscernible) and
developing (indiscernible) of course. (Indiscernible) So those were
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resampled again.
Focus areas, it was originally planned to do ten focus areas.
We did seven in 2013, and we repeated the sampling in 2014, in July
and September, for those focus areas. For water I mentioned, we
took four in 2013 and we've already taken the other six and we have
that data. 2013 data was all very good and we expect the same for
data for which we're currently providing the QA/QC.
As I mentioned before, thermal infrared, we took 72 percent of
the river and I think in 2013, 20 percent of the river in the middle of
the section between the project river model, 7890 approximately.
We didn't get in 2013 because of weather conditions. We were
planning to take it this year, but because of the amount of data we
had on temperature from the water quality study and the groundwater
information, it was determined that that wasn't going to give us
added value so we held off on that this year so we didn't take that last
segment. It wasn't going to give us added value and we had the
information that was going to help us.
So that's that and we'll open it up for questions.
The next talk is the modeling, 5.6, which is the water quality
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monitoring, so we can (indiscernible) back and forth with that..
UNIDENTIFIED FEMALE: (Indiscernible - over-
modulating.)
MR. PADULA: Is there a question on the phone for Harry?
UNIDENTIFIED FEMALE: (Indiscernible - over-
modulating.)
MR. PADULA: Oh, were you not getting -- you weren't
hearing this?
UNIDENTIFIED FEMALE: (Indiscernible - over-
modulating.)
MR. PADULA: Okay. So any questions for Harry based on
what you've seen or seen and heard?
Yes.
MS. VERBRUGGE: This is Lori Verbrugge from US Fish &
Wildlife Service.
Is that better?
Okay. This is Lori Verbrugge from the US Fish & Wildlife
Service, and I wanted to ask a little bit more about the analytical
problems in the water quality data.
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UNIDENTIFIED MALE: (Indiscernible - over-modulating.)
MR. PADULA: Can you hear us, John?
UNIDENTIFIED MALE: (Indiscernible - over-modulating.)
MR. GIBBONS: I'll repeat the questions, John.
So the current question is, is about some of the analytical or
sampling problems we had and what's happened to that.
MS. VERBRUGGE: And yes, specifically, I have a couple of
questions about the specifics of it, specifically about the total metals
and the total mercury. And was it only water samples that were
affected, or were other matrices also affected by analytical problems?
MR. GIBBONS: The sediment samples that we took in 2013
both (indiscernible) were QA/QC’d and fine and valid and we're
moving forward on that QA/QC now, but we think that's going to be
fine. It was the water quality samples for the total metals, except for
calcium and magnesium, that proved to be problematic in terms of
the analytical procedure yielding false positives due to the turbidity
and glacial flour and interference creating a false -- a higher level
than reality so we wanted to double-check that and come up with
ways to resample and see if we can get a better handle on that data.
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MS. VERBRUGGE: What percentage of your water samples
were affected by this problem?
MR. GIBBONS: The samples that had turbidity, I don't really
know, I'll have to get back to you on that.
MS. VERBRUGGE: Approximately.
MR. GIBBONS: The higher-turbidity samples all tended to be
high, and that's -- that is not uncharacteristic for a system that's like
this that has a lot of glacial flour. The White River for instance, that
was a real heartache for them to try go through the analytical
procedures to get an actual number that represented reality because
of the inferences.
MS. REEVES: This is Mary Reeves, Fish & Wildlife Service.
Were those samples filtered in the field or were they taken in
bulk in the field?
MR. GIBBONS: We took -- for totals they were taken in bulk
and we did try filtering stuff and so we did different procedures that
were -- several things that we weren't sure really good in 2013
relative to the total metals because of the interferences even though
they were filtered and some other (indiscernible) preservative and
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that sort of thing, that we wanted to overcome with the samples and
found that it wasn't quite up to where I wanted them to be. So that's
why we took them again in 2014.
MS. VERBRUGGE: And are we going to be able to see the
actual laboratory reports so that we can get a better understanding?
MR. GIBBONS: Yes, you'll see both the raw data from the
QA/QC data from 2013 with the spreadsheets with all the qualifiers
and all 2014 also will be given -- presented and with all the qualifiers
that we had to finish our QA/QC.
MS. VERBRUGGE: Do you have an expectation of when that
will be?
MR. GIBBONS: The 2013 data we're going to try to get it up
on the Web site. We're hoping to have that up in the next few to ten
days, and that -- the 2014, we're still finishing the QA/QC, so that'll
be done as soon as possible and I'm hoping to get it done by the end
of this year.
MS. REEVES: Yeah. To that, and there is a lot of data, and
right now, one of our thoughts is it's pretty difficult to evaluate
because it's not organized as well as it could be. It sounds like you're
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working on that, which is great.
MR. GIBBONS: Correct.
MS. REEVES: And maybe we can even -- if we can request
kind of format that we include a spatial limitation, you know,
(indiscernible) lat-long media, maybe an analyzed sample limit of
detection, and then lab qualifier with your lab qualifier, were there
field concerns for the sample, because it seems like there are also
some field sampling.
MR. GIBBONS: That's in our database currently.
MS. REEVES: Okay. And then it can all be in one place?
MR. GIBBONS: Should be, yes, we want it that way. The
whole idea is to get the information out.
MS. VERBRUGGE: Did you have other issues with the fish
samp les?
MR. GIBBONS: Well, fish samples, we didn't take the
samples. We got them from other studies and we took them to the
lab. The QA/QC for like total mercury count on fish tissue, we had
good analysis there. It was really more of how many fish were going
to be collected and it was more for mercury testing.
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MS. NOLAND: This is Laura Noland with Environ
International Corporation, and I have a question about the data
quality reports, which I did review, not comprehensively, but I did go
through them.
It did seem that in reviewing the COCs, that you were having
issues with delivering the samples within temperature limits, and
other issues as well that indicated you might be having field
sampling issues. [I had a question about the data quality reports
which I did review. It seemed that in reviewing the COCs that you
did have issues delivering the samples to the lab within the correct
temperature range? Could you give an estimate of what percentage of
these samples were out of temperature range?]
MR. GIBBONS: Yeah, there were some field sampling issues,
but given the amount of percent of issues with those samples, it was
a small percentage of the total data base. That was part of the
concern. Our concern was the analytical (indiscernible.)
MS. NOLAND: Do you have an estimate of what percentage
of those field samples?
MR. GIBBONS: Not off the top of my head. We can look at
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that.
MS. NOLAND: Well, I just want to --
MR. GIBBONS: It was pretty small.
MS. NOLAND: I don't think I agree with that, that it is
reasonable. But we will wait for the final report.
MS. REEVES: And this may be saying the same thing that
you just said, but it would be really nice to have a data quality report,
so some sort of synthetic document that says, that describes you
know, what happened, what bad things happened in the field with
your filters or whatever, and how many samples that affected, what
happened in the lab, how many samples were affected. If we can
have that kind of as a data formally following the report, that would
be really helpful to try to understand.
MR. GIBBONS: We did have DVRs for the 2013 data
included with the ISR for 2013 data and we’re producing DVRs for
the 2014, so you’ll have that.
MR. CONDER: You took the words right out of my mouth.
I'm Jason Conder with Environ.
And I echo their concerns. You know, we think the data
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reports and lab reports is great, but I think, you know, what we really
want to understand is we want to get to the same place where you are
when you look at the data and say this data is not a represented
reality. We want to, you know, we want to hear the thoughts of the
chemist, kind of the situation with glacial flour and the other
interferences that we might see and kind of the technical reasons
why the data just don't make sense, so I'm looking forward to seeing
that.
MR. GIBBONS: Yeah. I'll use an example, for instance, total
phosphorus, total phosphorus was in the milligrams per liter and the
high micrograms, several hundred micrograms to two -- up to
2-point something milligrams per liter in the system. Now, our
chlorophyll never got above 3 milligrams, you know, per liter. So
looking at a worldwide average, .3 chlorophyll to total phosphorus,
3 micrograms compared to 3 milligrams is a few orders of magnitude
off. So that's a reality check that's we have to figure out what's going
on.
MS. REEVES: So that suggested to you that it wasn't
dissolved in water, that the phosphorus wasn’t dissolved.
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MR. GIBBONS: The dissolved phosphorus met all QA/QC.
(Indiscernible) that was given was very, very low.
MR. KRISTANOVICH: Felix Kristanovich from Environ.
Two questions.
The QAPP report was issued partway. So in your analysis, the
2013 data, it didn't have a QAPP with it, am I correct in that?
MR. GIBBONS: No, we had a QAPP and we followed the
QAPP, that's correct.
MR. KRISTANOVICH: You had a QAPP (indiscernible).
MR. GIBBONS: We have a QAPP, and remember, QAPP
(indiscernible) design has addendums filed to it as there are variances
and changes and modifications. So, yeah we had it in place.
And part of our rigorous QA/QC, it's spelled out in detail.
MR. KRISTANOVICH: The second question comes back to a
presentation from one of the technical meetings that was presented in
(indiscernible). Apparently there was a mess up in one of the labs. I
never found (indiscernible) an explanation of actually what happened
with the labs in the ISR. Can you elaborate on that?
MR. GIBBONS: Well, for instance, the total phosphorus that I
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used in a previous example, there's a lot of false positives being
generated by the glacial flour, particularly the colloids and clay
particles, but also arsenic and other things, and that’s very similar to
other studies we’ve found with glacial flour where you get false
positives in the analytical procedure for the phosphorus. So that's
what we're trying to straighten out.
MR. KRISTANOVICH: But that's the reason the results from
the two labs are completely different?
MR. GIBBONS: Yes. And there were some other interfering
problems too. The results are in the database.
MS. VERBRUGGE: I think I'm thinking of the same
technical meeting that you're talking about, and there was some
discussion about whether preservative was or was not in the
containers and it wasn't --
MR. GIBBONS: We did. We did test on the preservatives in
the sample bottles at the filtering and non-filtering levels and also the
blank samples from some of the labs, and so there were some issues
with the 2013 data at several different points.
MS. VERBRUGGE: And the discussion of that will also be
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included in your QA report?
MR. GIBBONS: Yes, right.
MR. PADULA: (Indiscernible - distance from microphone.)
MS. LANCE: Ellen Lance, Fish and Wildlife Service. My
question goes back to our discussion from earlier today, Wayne. So
what I'm hearing is that the 2013 data will be available in about ten
days, and the 2014 data won't be available until the end of this year,
which won't leave us very much time to consider this data prior to
our February 23rd deadline.
So I'd like to request and ask if it's possible for us to get that
data sooner, and if so, what date can we expect it?
MR. GIBBONS: It's a lot of data we're going through, so
we're trying as hard as we can, as we qualify the data and they pass
the QA/QC, we'll be trying to get that to you but I can't give you a
date right now.
MR. DYOK: Ellen, I hear your request here. I just -- I know
that they've been working very hard on this issue. I just want to
make sure that everything goes through the proper QA/QC, you
know, process , you know, first, but we'll just try to stay tune with
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Harry, but I think he's given you probably a reasonable estimate on
when he is going to get that done. I think it would be really tough to
expedite that.
MS. LANCE: Ellen Lance, Fish & Wildlife Service.
I understand. My concern is that we won't have all the
information to -- prior to potentially making a modified study
request.
MR. GIBBONS: I understand.
MS. NOLAND: This is Laura again, Laura Noland with
Environ.
Could you just summarize the challenges with the 2013 data
and how you corrected the issues that you had in 2013 when you
went into the field for 2014?
MR. GIBBONS: There were a multitude of issues. One and
the largest was a consistent false positive, for, for instance Kjeldhal,
the (indiscernible) detection was too high. So Kjeldhal in 2013 we
got very few Kjeldhal nitrogen detections in the reports, and we
knew from looking at the data and other things that we have
Kjeldahl. So by lowering the detection limit and going to another lab
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that had a routine to get low-level nutrients , we were able to get the
Kjeldhal data for 2014 and it’s coming out to be about 220, 280, and
our detection limit (indiscernible) was 310. So that’s one problem.
The false positives of the glacial flour and other issues in the
glacial flour, total metals, total phosphorus and others, that was the
major analytical problem that we faced, and so we've gone through
several techniques with an additional lab who has experience with
that to try come back in 2014.
MS. NOLAND: Okay. One last question. Have you amended
your QAPP based on the 2013 experience?
MR. GIBBONS: We have amended them. I don't think we
have officially filed that yet.
MS. NOLAN: Thank you.
MR. GIBBONS: We will also have, you know, where we
can't resolve an issue analytically, we will have the data sets that we
will find ways to correct the data to represent (indiscernible.)
MR. MUNTER: This is J.A. Munter with J.A. Munter
Consulting.
Can you elaborate a little bit on some of the technical factors
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that went into the decision to not put back a thermal IR imagery?
Was it not working or you already had data in that area? I’m going
back to one of the comments you made that was pretty brief.
MR. GIBBONS: Yeah. We -- in 2'13, we couldn't collect all
the data because of weather conditions, and the middle reach of the
river we didn't collect. We were scheduled to collect it in this year,
but we held off because we had a lot of huge database in terms of
direct temperature measurements from both the water quality and the
groundwater study, and we had already been in the field to do the
observations to kind of understand where things were. And Dudley
sent an e-mail saying, you know, we're pretty much okay, we don't
need this data so let's hold off on that. It wasn't going to give us
added value so we saved some money because of the logistics.
MS. REEVES: Mary Reeves, Fish & Wildlife Service.
Can you clarify, you're using the term a lot. You're saying
false positive. And to me that has a pretty specific connotation,
which is that you are seeing something in your sample which is not
in the sample bottle. And I -- but you keep saying it in conjunction
of glacial flour.
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So can you clarify what you mean by that? I mean, is it
possible that there is a lot of arsenic for example, (indiscernible) but
in the flour itself and you only see the flour, but you wanted to
sample the water, so it was really that field sample that really didn't
allow you to distinguish. Because to me, that's not a false positive.
That's more of a -- if you could speak to that issue.
MR. GIBBONS: Yeah. It's funny you bring up arsenic
because that's one of the parameters we're looking at, the phosphorus.
MS. REEVES: Use that (indiscernible).
MR. GIBBONS: Okay. Yeah. Because it's giving -- it
mimics in a colorimetric test for total phosphorus it is a false positive
generator and we are getting levels of arsenic that are helping in
terms of increasing (indiscernible). So those are the type of things
we're trying to sort out. And yes, we're trying to do that.
Also, trying to get out what is the true arsenic total. In both
(indiscernible) inside. We are trying to get out what is the true total.
MS. REEVES: That helps to clarify those issues in the data
quality report would be very helpful as a summary of what you found
regarding those issues.
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And then I have one follow-up question. Because sampling
for contaminants obviously you're looking at very low levels of
things like metals, parts per billion often in water, and so the
potential , it's critically important how you handle those samples. I'm
sure I'm preaching to the choir, but I'm wondering, I also know this is
a very logistically complicated project, and I'm wondering if
anywhere it could be provided in the data quality report how many
different samplers there were and how many different groups doing
all the water quality, were different people doing sediment sampling
that water quality sampling and what was the level of training of the
field personnel? I'm not questioning but I think it would be really
helpful to be able to see that as we move through the data.
MR. GIBBONS: We put that in as (indiscernible). It was
basically the same team, different teams at different times, so the
water quality team rotated so we had a mix but all trained at the same
level and our sediment was taken by the same two individuals both
years that were part of the water quality team as well. We tried to
avoid as much -- because this is so complicated, so many samples,
40,000 samples.
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MS. REEVES: I know. I emp athize.
MR. GIBBONS: We wanted to make sure. Those things
weren't biting us too bad.
MS. REEVES: I hear you. Been there.
MR. PADULA: Any additional questions for Harry? On the
baseline water quality study?
Okay, hearing none, we'll move on.
John, you're going to do the presentation from the phone?
John Hamrick, are you on the phone?
MR. HAMRICK: Yeah, this is John. Sorry, I was on mute.
Yes, I will be doing the presentation on the phone and Harry will be
doing the slide.
MR. PADULA: Great. Can you see your first slide?
MR. HAMRICK: Yeah.
WATER QUALITY MODELING (STUDY 5.6)
MR. HAMRICK: Can you hear me well?
MR. PADULA: Yes. Coming through loud and clear.
Thanks.
MR. HAMRICK: Right. Let's go to the second slide, Harry.
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Just to highlight the objective of the water quality modeling study,
basically modeling both the reservoir and the river temperature and
the reservoir river water quality which would include (indiscernible)
organic matter, chlorophyll.
And of course, the approach is that the river will be modeled
both under pre-project conditions and post-project conditions and the
reservoir model will provide the (indiscernible) conditions for the
(indiscernible - distance from microphone).
Again, the (indiscernible) will be brought in from the
(indiscernible).
Next slide. Just the components (indiscernible), description of
the models, modeling approach, special focus area modeling we'll
use higher resolution and focus area and (indiscernible) output.
Next slide.
We implemented the (indiscernible) that are described in the
study plan with no variances.
Summary results. This is really -- this slide is sort of a -- more
of a recap of the state variables that's split between the two models.
(Indiscernible) temperature of TSS, (indiscernible) organic matter
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(indiscernible)
Next slide.
Summary of results, the reservoir model has been configured,
has 20 layers and vertical has about (indiscernible). We have
demonstrated the reservoir model to be robust being able to simulate
multi-year periods where we have almost (indiscernible) variation
river model (indiscernible) in the ISR was configured to downstream
project river mile 80 (indiscernible).
Next slide.
For the river model, we again basically simulated multiple
(indiscernible) periods. Stay with me a minute. (Indiscernible.)
MS. MCGREGOR: I think he’s having technical issues. He said he lost
the presentation.
MR. PADULA: John, what's up there?
MR. HAMRICK: I've lost the (indiscernible - interference
with speaker-phone) come back. (Indiscernible.)
MR. PADULA: That would be great. Just let us know which
slide you're on.
And when you're speaking, you tend to fade out, so if you can
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try to maintain consistent volume there, that would be great.
MR. HAMRICK: Okay. I think we should be on Slide No. 7.
MR. PADULA: Correct
MR. HAMRICK: And I was there discussing river modeling
results, again demonstrating (indiscernible) to simulate multi-year
periods looking at pre and post project conditions and their
evaluating differences. The pre-project river models will be, or is in
the process of being calibrated to data collected between 2012 and
2013, and 2014 data will be sort of brought into play as it becomes
available.
Next slide, Slide 8.
These are results since the ISR. Some of this may have been
presented as proof of concept B. The reservoir model was used to
simulate (indiscernible) 1976 was a dry year period and 1981 was a
wet year. The main results of the reservoir simulation here show if
we, the maximum load (indiscernible) scenario, (indiscernible)
operation of the (indiscernible) somewhat warmer water coming out
of the reservoir.
The other thing that we had simulated or looked at so far is we
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actually had an inflow of fine sand and some clay-size material. We
found that the -- with the water (indiscernible) from the surface land
to reservoir, we found that the fine sand is almost entirely retained.
There is a significant retention of the clay.
Slide 9. The river model was extended down to project river
mile 29.9. We did the same two sets of pre-year simulations, again,
over the full range of the river from the reservoir to the 29.9.
And again, we looked at the difference in pre- and post-project
temperature to 29.9. I can't remember at this point if the technical
memo actually shows both three-year periods, but this is just an
example of looking at a correlation between pre- and post-project
temperature. Generally they differ by less than 1 degree at project
river mile 29, again the technical memo shows how temperature
differs at various (indiscernible) down the river and (indiscernible).
The TSS in the middle river will likely be much lower due to
significant trapping of all of the fine sand (indiscernible).
Slide 10, please. Focus area modeling. The focus area
modeling that we're conducting goes very much along the same lines
as that being done at the geomorphic study. We are planning, of
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course, to do dynamic simulation rather than (indiscernible) sort of
base flow so we'll have to use somewhat coarser resolution for a
longer term time for dynamic simulating. One thing we're going to
do is maintain consistency of the (indiscernible) between the other --
the two (indiscernible) and the two (indiscernible) are the focus
there. We're currently completing the (indiscernible) for focus areas.
(indiscernible) demonstrated for the seasonal scale stimulation for
those two.
The proposed modification for the study, we have no
modification for the study plan.
Slide 12. Decision points (indiscernible), same decision point
as the geomorphic modeling. We’ve reached a similar conclusion
that the quality model will not be extended downstream of project
river mile 29.9. That decision is based on the analysis and
comparison between pre- and post-project temperature at that
location where (indiscernible) slide in the technical memorandum
show less than 1 degree difference between scenarios, 1 degree
(indiscernible), and also that the (indiscernible) river at that point
(indiscernible) much of (indiscernible). Of course (indiscernible)
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sufficient data behind the 29.9 but that was not a major issue in the
decision point. And this, again, is documented in the technical
memorandum.
Slide 13. Just a current status. I will try to go through all of
these quickly, but it says we have completed configuration of the
reservoir model. We did not plan to change the model
(indiscernible) or the resolution. We've shown that we have done
multi-year temperature and fine sediment simulation. A somewhat
simple ice model to be sort of implemented and tested which will
primarily be a (indiscernible) model that I suspect will cover using
something a little beyond our reaches for today.
Again, the water quality model configuration is under way.
We'll continue into the next calendar year as the additional water
quality data in 2015 become available. Toxic and mercury model,
again, will -- hasn't been started because most of the work will be
done the early part of next year.
The reservoir doesn't exist. It cannot be calibrated.
(indiscernible) sort of documentation of the robustness or the
performance of the reservoir (indiscernible) high latitude or high
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altitude reservoir. The reservoir model is able to, you know, rapidly
change scenarios and incorporate scenarios based on the 60 year
hydrologic period (indiscernible) looking at outflow levels and
(indiscernible).
Slide 14. Again, the river model (indiscernible) configuration
in 2013. Final configuration, what we call the four-year model,
where this year it was stopped at 29.9. The -- we'll be looking at
things for importing ice (indiscernible) from the ice processes model
in the middle river. Right now the river (indiscernible) does one for
through the year. It's the water temperature does come slightly above
(indiscernible) to the reservoir model (indiscernible) to the
(indiscernible).
I might note too that the calibration of the river (indiscernible)
pre-project (indiscernible) the river model can be calibrated with
(indiscernible)
Slide 15, please. Focus area modeling. Sort of developed
what we'll call a higher resolution grid for the focus area
(indiscernible) independent (indiscernible) river model. We
(indiscernible) that will be sort of (indiscernible) focus areas
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(indiscernible) and focus area (indiscernible). Again, we developed
(indiscernible) to provide data to (indiscernible) temperature
(indiscernible) and some (indiscernible) divisions indicate the river
(indiscernible). Again, (indiscernible) scenario stimulation
(indiscernible) the reservoir (indiscernible).
Last slide.
MR. PADULA: Thank you, John. We'll hopefully get some
questions for you to answer.
Anyone want to start? Identify yourself, please, folks.
MR. KRISTANOVICH: Yeah, this is Felix Kristanovich
Environ International. I have a number of questions, so maybe I
can just go one by one if that's all right.
Yeah. My first question is with respect to your model
[calibration]. I think originally we were expecting for it to be
finalized now. It's being postponed? And I see that now [you’re
calibrating with] 2012 and 2014. Wasn't originally it was supposed
to split [one part for calibration and one part for validation]? That's
the first part of the question.
Second part of the question, I think this is really important.
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How confident are you right now to (indiscernible)? You are not
complete (indiscernible). How are -- how confident are you in your
important decision that you have made, based on the results of the
model?
Like, for example, not extend model past 29.9. [How confident
are you in the decisions to not extend the model downstream of 29.9?]
MR. HAMRICK: I (indiscernible - interference with
speaker-phone) or the river, or both?
MR. KRISTANOVICH: For the [riverine model].
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) of the river model (indiscernible) or the open water
(indiscernible) model, and also (indiscernible) transport model, that
there can be a calibration validation process for (indiscernible)
discharge and velocity at certain locations. Likewise, the
temperature -- the temperature component of the river model is being
calibrated to the (indiscernible) open water period.
We likewise (indiscernible) calibration period (indiscernible)
in the approach (indiscernible) two years, and so I hope that
(indiscernible). My apologies (indiscernible), but (indiscernible).
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MR. KRISTANOVICH: Can we at least see some preliminary
results of calibration? Because you are providing us with a model. I
mean, we probably did some calibration to something that we at least
can see.
MR. HAMRICK: Yes, they're not -- at this point they have
not been put into -- they are not in the technical memorandum, which
primarily focused on the decision point issue regarding the extension
to 29.9.
MR. KRISTANOVICH: I'm going to go ahead with some
other questions. [I was disappointed not to find any information
regarding the development of the mercury model I remember that at
the last meeting you were anticipating it being done in the next 6
months. Do you have anything or are you anticipating this in the
next year?]
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) model, we are (indiscernible) mercury level was
(indiscernible) water quality model (indiscernible) predictions. So
the (indiscernible) process of developing the -- developing the
(indiscernible) organic material that was going to be (indiscernible)
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primarily from shallow areas where there is vegetation.
MR. KRISTANOVICH: The next --
M: (Indiscernible - interference with speaker-phone) sulfides.
MR. HAMRICK: (Indiscernible - interference with
speaker-phone.)
UNIDENTIFIED MALE: (Indiscernible - interference with
speaker-phone) sulfides.
MR. HAMRICK: That (indiscernible - interference with
speaker-phone) to be determined. I think maybe (indiscernible)
better to be (indiscernible) following presentation.
At this level, I don't -- I don't foresee doing that, but that could
change if there's different information and sort of the analysis of
(indiscernible) -- the analysis of the information that will allow a sort
of (indiscernible.)
MR. PADULA: John, could the person who asked that last
question identify themselves?
UNIDENTIFIED MALE: I'm (indiscernible).
MR. PADULA: Say that again, please.
UNIDENTIFIED MALE: (Indiscernible - interference with
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speaker-phone.)
UNIDENTIFIED MALE: (Indiscernible.)
MR. PADULA: Okay. Thank you.
MR. GIBBONS: Just to clarify what John's saying is we're
still finishing the pathway models and putting that together and we'll
adjust sulfides relative to the (indiscernible).
MR. KRISTANOVICH: Can we get a timeline
(indiscernible.) spend time on this (indiscernible)?
MR. GIBBONS: Yes. We'll be able to discuss and present in
January the (indiscernible) model. We're going to put it together by
December, have a QA/QC by one of our colleagues and John on that,
in terms of fine-tuning the mercury model based on those pathways
and then we'll before the January meeting an independent technical
review of that pathway.
MR. KRISTANOVICH: Thank you. I'm going to have
another question to ask.
[Have you done any sensitivity analysis to other operations
that would show us any sensitivity results?]
MR. HAMRICK: (Indiscernible - interference with
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speaker-phone.)
MR. KRISTANOVICH: (Indiscernible - distance from
microphone).
MR. HAMRICK: That (indiscernible) if you follow the
(indiscernible) of the reservoir (indiscernible) would typically be
colder than the (indiscernible) are going to (indiscernible) end up
with a sort of (indiscernible) there is a certain temperature there is
(indiscernible) follow the lead of the (indiscernible).
The other (indiscernible) the issue, I am looking at
(indiscernible) of the trapping (indiscernible) we're really confident
that fine sand is almost entirely trapped (indiscernible) trapping that
much of the silt (indiscernible). I am looking at whether you can
simply lump silt and clay into sort of a single (indiscernible)
sediment category and assign a (indiscernible).
However, if you do have some information (indiscernible)
three or four (indiscernible), then you may get (indiscernible). And
certainly, I think that's sort of (indiscernible). We haven't -- we
haven't said the (indiscernible) in the river (indiscernible) any effect
on (indiscernible) penetration or (indiscernible). So that's
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(indiscernible).
MR. KRISTANOVICH: Thank you. [I would like to mention
that we will review technical memorandums in more detail and you
may get more questions because this could have tremendous impact
downstream and on other studies.]
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) are you referring back to.
MR. KRISTANOVICH: (Indiscernible - microphone
feedback.)
MR. HAMRICK: (Indiscernible - interference with
speaker-phone.)
MR. PADULA: John Zufelt is indicating that they haven't had
a chance to review the latest technical memorandum, so there could
be additional questions for you.
MR. HAMRICK: Well, yeah, certainly, if it's (indiscernible)
make that comment again. My apologies for not being there
(indiscernible), but I certainly encourage everyone to -- I didn't
answer your question or I didn't hear on the phone, but
(indiscernible._
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MR. PADULA: Any additional questions for --
MS. REEVES: This is Mary Reeves with the Fish & Wildlife
Service.
I have two questions. I think one is probably broadly related
to model calibration. Could you explain how -- and I'm not so much
a modeler, so maybe you can kind of dumb this down, but how the
historic data fit into the model? You know, the data we collected 20
years ago, how the TIR data, for example, fit into the temperature
models. I'm using temperature here, but obviously the modeling was
for a whole bunch of different things.
And I would like to know whether those indeed are driving the
models, and if they are not driving the models, then how well the
models are matching up with those data. That's question one.
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) the previous study?
MS. REEVES: Yeah, like the '70s, '80s. I'm new to the
project too.
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) certainly, in terms of some aspect of (indiscernible)
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start at the beginning (indiscernible) information towards
(indiscernible) from the 50-year hydrology, which (indiscernible)
reservoir and (indiscernible). I think that's very wise (indiscernible).
For the next (indiscernible) temperature and say (indiscernible)
50-year period. We now know (indiscernible) correlation of
temperature (indiscernible) time of the year (indiscernible). We're
basically trying to identify a (indiscernible) temperature
(indiscernible) particular data (indiscernible) model back
(indiscernible). Basically the (indiscernible) Talkeetna has
(indiscernible) long-term National Weather Service station, and that
does go back (indiscernible) correlating back with (indiscernible)
current data to (indiscernible) and to also (indiscernible) how we're
using some of the data.
MS. REEVES: Okay. Thanks. That's good. And I think that
will probably get laid out more clearly and kind of as we are able to
incorporate these 2014 results and consider them, so I hope that those
kind of linkages are very clear as we move forward.
And my second question is, you obviously -- one of the main
questions here is how do things change, and the time for example
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fish eggs that needs to hatch between a certain -- within a certain
temperature envelope. In that case, the variation in temperature may
be more important to me than predicting an average value. There are
some cases where it's very useful to see one line that shows the
average, and then there are other cases where it's more useful to see
kind of an envelope around that line of uncertainty in your estimates.
And I think in the case, for example, biological resources, like fish,
that that envelope that shows your uncertainty is very important.
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) time scale I (indiscernible) high resolution
(indiscernible) so there are (indiscernible) probability that can be
(indiscernible) the average (indiscernible) or the variability of that
(indiscernible) habitat starting (indiscernible) provide the
information for that (indiscernible) process that is
(indiscernible - foreground conversation).
MS. REEVES: So what I'm hearing you say is that it is
possible in the modeling exercise that we're doing to predict not just
the average value, but uncertainty values around the estimates?
MR. HAMRICK: (Indiscernible - interference with
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speaker-phone) hydrologic and climatological (indiscernible) can be
looked at (indiscernible) compare that with (indiscernible) all the
information that can be extracted.
MS. REEVES: Right. And so we would -- I guess this is my
request, that we are able to see and evaluate that kind of variation as
we move forward, and we would like to see the linkage made from
the field data that was collected at specific points to what the model
is predicting at those points so that we can also see how well those
are matched up.
MR. HAMRICK: And (indiscernible - interference with
speaker-phone) pre-project, post-project on a day or an hour-by-hour
basis at this location, it would really be more appropriate to sort of
compare the means or expected values and the variability.
MS. REEVES: Yes.
MR. PADULA: Thanks, John.
MR. MCLEAN: This is Dave McLean from Northwest
Development. So my question is related to the reservoir model, and.
[Related to the reservoir model and this also relates back to water
quality modeling replacing the need for geomorphic studies in the
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reservoir. How does water quality overlap with sediment modeling?]
MR. HAMRICK: Okay. I think I understand
(indiscernible - interference with speaker-phone) the geomorphic
model (indiscernible) should be -- should the reservoir be modeled
(indiscernible). The modeling (indiscernible) has, let's say, a
complete (indiscernible - foreground conversation) the geomorphic
study (indiscernible) there are influences (indiscernible) any potential
(indiscernible) in those kind of situations and (indiscernible).
MR. MCLEAN: You've answered some of my questions but
maybe I can just go through some specific questions.
[For a sedimentation model we would normally run a model
for 100 years or longer to look at patterns of deposition. Regulators
ask for 1,000 years of data from a model. Not trying to critique your
water quality model. How are we going to learn about sedimentation
and geomorphology from this model? Is it morphodynamic? How
do you handle that aspect of it.]
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) depends on the (indiscernible) prediction and the
(indiscernible) would lead to this model for representative
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(indiscernible).
MR. MCLEAN: Yes, I'm not trying to keep your water
quality modeling, I'm not qualified to do that, I'm not (indiscernible)
presentation. I'm just trying to figure out how we're going to learn
about sedimentation processes and geomorphic processes from this
very sophisticated model. That's the way I'm approaching it. So
(indiscernible) the model (indiscernible) and does that feed back into
your (indiscernible)? How do you handle (indiscernible)?
MR. HAMRICK: Actually (indiscernible - interference with
speaker-phone) dynamic. It can involve (indiscernible).
MR. MCLEAN: (indiscernible - interference on microphone.)
MR. HAMRICK: Other than the (indiscernible - interference
with speaker-phone) at the reservoir site (indiscernible) the model
could be updated to (indiscernible).
MR. PADULA: Okay. John, hold on. Another question
coming.
MR. MCLEAN: (Indiscernible - interference on microphone)
[When you run the model now is it actually doing the updating?
With some models you have a choice and you can decide when you
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do the updating of the bathymetry and it’s much faster to run the
model when you don’t. You have run multiple year simulations. If
bed loading is not that important certainly in decades it becomes
more critical.]
MR. HAMRICK: Right.
MR. MCLEAN: (Indiscernible - interference on microphone)
so in that case, do you bother to (indiscernible) for centuries
(indiscernible).
MR. HAMRICK: Boy, yeah. (Indiscernible - interference
with speaker-phone.)
MR. MCLEAN: Thank you.
MR. HAMRICK: But that sort of crosses the line between the
geomorphology and the reservoir study and as I said, it's not
(indiscernible.)
MR. PADULA: Thanks, John.
Sue, a question?
MS. WALKER: Yeah, John, this is Sue Walker. I have a
question.
As I understand it, the model temperature increase assumes
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static conditions. It's based on past and current temperatures, yet we
know that water is warm and will continue to warm.
So I have two related questions. One is, how does your model
project future water temperatures without the project? And then a
related question, how does your model project future water
temperatures with the project knowing that water temperatures will
continue to increase independent of the project, and that
project-induced increases in water temperature are on top of, or in
addition to, the shifting baseline of continuing environmental
warming? [What are you doing to account for that?]
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) summarize but I got the point. (Indiscernible) shows
the (indiscernible).
MS. WALKER: Slide 8?
MR. HAMRICK: (Indiscernible - interference with
speaker-phone.)
MS. WALKER: He didn't understand the question.
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) takes a lot to heat up a (indiscernible) mass but once
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you get into the summer, though (indiscernible) reservoir, we heat it,
we do have a therma (indiscernible) actual temperature conditions in
the river (indiscernible).
MS. WALKER: Thanks, John. I don't really think that
answered the question, though. That -- your model was using past
and current temperature data to project future reservoir temperature
scenarios. It's -- you mentioned climatologically significant years,
cold, dry years, but it doesn't seem to be recognizing climate trends,
which are clearly known and identified.
So I think a better question is, is information from Study 7.7
going into this modeling? It's inappropriate to assume static
conditions in terms of temperature.
And the same question applies for the modeling of future
reservoir conditions and for the outflows. So just very basically, is
climate information from Study 7.7 going into your reservoir
temperature models in your downstream temperature models?
MR. DYOK: John, this is Wayne Dyok. Maybe I can help
you out a little bit on the --
MR. HAMRICK: Yes, I didn't respond to (indiscernible) and I
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certainly appreciate you jumping in here.
MR. DYOK: First of all, a couple of things, Sue, with respect
to the shutter operations, shutter operation, if we ask John
tomorrow --
MS. WALKER: I thoroughly understand the shutter
operations and that's not related to my question.
MR. DYOK: Okay. So you know that we can pull water at 4
degrees or near the surface?
MS. WALKER: Yeah. I appreciate that. I understand that,
but --
MR. DYOK: So your question is specific to climate change.
We are looking at combinations of meteorological from you know,
different combinations of cold years to warmer years, and you're
really referring to from a climate change, maybe a warmer type of
thing. We're looking at variability of precipitation with those, as
well. We can run sensitivity analysis that would deal with your
question.
The plan is to look at the meteorological and hydrological
conditions that we have expected to -- that we've seen in the past.
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That's part of the study plan. We can easily do a sensitivity analysis,
a what if you had 2 degree C, warmer temperature climate, okay?
So those are simple things you can do with this model.
But the plan is to look at the historic data first and model based
upon current conditions. But the model has enough flexibility to go
beyond that, if necessary.
MS. WALKER: Can I just respond that it doesn't need to be a
"what if". The climate is warming. That is documented. That is
fact. What's being done -- please let me finish. I don't want to hear
about shutters. I know that you can do that. I understand that
completely.
But the model being used to project future conditions without
the project, from which project conditions are being modeled, we
know is wrong. We do not have past and current conditions. We
have a trend of warming. That trend is not incorporated in this
model or in other models.
Mary, do you have --
MS. REEVES: Just as an example of that, there predictions
(indiscernible) that might be useful kind of date line where we could
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monitor (indiscernible)
MS. REEVES: And I did want to say that graph would be a
really good example of something that would really be nice to see,
kind of a confidence window on so in these reports that we're getting,
if you can see not just a red line, but a window around. That red line,
when you're having to start making decisions about effects on
biology, that window can be really important.
And I had one last question. You talked about stopping
modeling below river mile 29.9. That's a very specific number, and
so I'm wondering if you can discuss how you -- or describe how you
came to arrive at that number and whether there might be uncertainty
around that number, and if so, what that might be.
MR. DYOK: I think John needs to respond to that question.
It's more of a technical, you know, question.
And as we've said previously, just to deal with your climate
change question, we're going to have the information from the glacial
study. And so we have that information. We can look at that and
compare that meteorologic conditions and see if it's outside.
So we can actually, if necessary, and I'm saying that this is
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what the Alaska Energy Authority, you know, would do. It's not part
of the FERC study, you know, program here. But we can actually
use this model to look at and see, are we outside of what these
meteorologic conditions are, because we think that the broad range of
conditions that we're looking at is a broad range. We're looking at
different meterological and hydrological conditions.
We can look at what kind of in-flow temperatures we're
seeing. You know, John can look at -- run that in a small -- these are
simple things to do, but they take time and they take money.
Before we commit to those things, I would like to see the study
that we're doing -- work with you. Let's look at the results and
maybe there is value and maybe there isn't value in going to that next
level. But I think we have the tools to be able to do that.
MS. WALKER: Mary, may I respond, please?
This is Sue Walker. Wayne, I really appreciate that answer.
That does clarify it.
But in reading the studies, it's not clear that the information is
going into these modeled studies where temperature is so important
and is so biologically important. So knowing that you are going to
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look at those results and you are going to do a comparison is very
helpful.
Also, this is a great example that Mary brings up. You can use
the climate information available to put some confidence and
(indiscernible) around that to determine whether if there is a
difference in temperature from changing climate continued warming,
does that difference make a difference? It may not, but without
doing the analysis, you won't know. So I'm glad to hear they are
doing analysis.
MR. DYOK: And, John, could you answer Mary's question
regarding the extent of your modeling downstream to river mile
29.9? Do you recall the question?
MR. HAMRICK: Well, I think that in terms of the choice of
29.9, it is -- it sort of relies back to the geomorphology study also. ,
and it is just below the (indiscernible), which actually has a
(indiscernible) on the temperature.
We have looked (indiscernible) geologic study, the effect of
(indiscernible) temperature on the dam has (indiscernible) the dam
outflow temperature (indiscernible) I would say (indiscernible) 1
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degree, at most, temperature (indiscernible) project. The technical
memo actually shows that (indiscernible) current condition shows
that the (indiscernible).
UNIDENTIFIED FEMALE: (Indiscernible - interference with
speaker-phone.)
MS. WALKER: Is someone calling their dog?
MR. PADULA: There's someone else on the phone with some
background noise. If you'd mute yourself, we would appreciate it.
MR. HAMRICK: But yeah (indiscernible - interference with
speaker-phone) it's a little more complicated (indiscernible) to see
that (indiscernible) and again we see that by the time we reach this
point, the difference in temperature is quite small and the
(indiscernible) is quite small.
But (indiscernible) becomes quite complex (indiscernible) so
there may be some (indiscernible) still might be some effect
(indiscernible).
MS. REEVES: (Indiscernible - distance from microphone.)
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) is a gauge station and (indiscernible).
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MS. REEVES: Can I repeat back to you, just to make sure I
got what you just said?
It sounds to me like there are three factors that you're -- that
are feeding into this 29.9 decision.
One is data, that you don't have as much data below this point.
That was kind of a minor point.
Another was river complexity below this point, that it's hard to
model the channel below this point.
And it sounds like the third one is variation between
temperatures with the project and without the project. I heard you
say that this was the kind of that threshold point (indiscernible). [Are
the three factors feeding in to stopping at 29.9- 1) The data, not
much, that’s a minor point. 2) River complexity –It’s harder to model
the channel below this point, and 3) the other is variation between
temperatures? There is variation pre- and post-project as an estimate
at river mile 29.9. I would like to see the variation around that
estimate according to your model for example how many miles back
and how many miles forward would you like to go, how confident
are you in that you stabilized that. I’m interested in seeing a better
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variation of temperature and interested in seeing what the models are
predicting at the spatial and temporal scale. Describe your level of
confidence in your estimates does it go from 25-35 or 20-40 how
confident are we? It would be helpful to see three maps for example,
this is my low and this is my high estimate. Also, it would be helpful
to see longitudinal profiles and temperature as flow goes downstream
so you can see different kinds of differences and figure out specifics.]
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) other things, like we don't have cross sections yet or
(indiscernible).
MS. REEVES: Okay. So --
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) analysis (indiscernible) study. I (indiscernible) 29.9
(indiscernible).
MS. REEVES: Okay. And so to follow up, so say that this
variation pre- and post-project you've got, again, reporting an
estimate of river mile 29.9. What I would like to see is the variation
around that estimate according to your models, how many miles back
and how many miles forward can we -- might we go? Like how
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confident are you on that 29.9 that you have stabilized the
temperature between pre- and post-project?
And this basically underscores I've already put in a request to
have a better visual demonstration of temporal variation, so like the
charts up there on Slide No. 8, I'd like to see a (indiscernible). We'd
also really like to have --
MR. HAMRICK: (Indiscernible - interference with
speaker-phone.)
MR. PADULA: John, hold on, let her finish, please.
MS. REEVES: I'd like to have an understanding of partial
variation, and your level of confidence. Because one of the things
that I think we understand about hydroelectric projects in the
(indiscernible) is that there can be a homogenization, ecological
homogenization downstream, where we change those characteristics,
and we're interested in seeing what the models are predicting about
what your spatials -- your spatials (indiscernible) spatial and
temporal (indiscernible). Does that make sense? We'd like to you
describe your -- your level of confidence in your estimates.
So for example, the estimates 29.9 I would like to confidence
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(indiscernible) 25 to 35, or does it go from 20 to 40? You know,
how confident are you at that point? But I just need kind of spatial
(indiscernible - foreground conversation), and it's (indiscernible).
MR. DYOK: Yeah, I think I know where you're coming from.
And essentially (indiscernible - foreground conversation)
temperatures as (indiscernible) kinds of differences. And we need to
sit down and figure out the specifics of what we're going to look at),
but I think typically John (indiscernible) is to look at a particular
point in time and at a particular location and then see how water
temperatures are (indiscernible - foreground conversation) snapshot
of the river and we're looking at how (indiscernible) post-project
condition and (indiscernible) should be a representation of the
(indiscernible) confidence (indiscernible).
And just kind of mention that we might want to look at the
technical memo that John's put together on the basis for his curtailed
involvement (indiscernible) 29.9 that got submitted (indiscernible).
MS. REEVES: Yeah. And this -- and I know we're talking
about changes again, which we don't want to talk about. But I
thought that since I had the opportunity, if you could answer the
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question, it would help me move forward.
MR. PADULA: Okay. One more from Sue.
MS. WALKER: Hi, John. This is Sue again. I have one more
question. Well, actually two.
You mentioned that at river mile 29.9, there is a 1 degree C
difference in water temperature. I assume that that's an average
annual temperature? And – [at RM 29.9 there is a 1 degree
difference in water temperature is that an average annual
temperature?]
MR. HAMRICK: (Indiscernible - interference with
speaker-phone) technical memo (indiscernible) temperature at 29.9
(indiscernible).
MS. WALKER: Okay. I understand now.
MR. HAMRICK: (Indiscernible - interference with
speaker-phone.)
MR. PADULA: (Indiscernible - distance from microphone.)
MR. HAMRICK: (Indiscernible - interference with
speaker-phone.)
MS. WALKER: (Indiscernible - distance from microphone.)
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MR. HAMRICK: (Indiscernible - interference with
speaker-phone.)
MR. PADULA: Thank you, John.
MS. WALKER: Thanks, John. I wasn't done with the
question.
Anyway, I appreciate that this is in your September tech
memo, which we of course will be looking at, and this is our first
experience. I understand the significance of this 1 degree in terms of
your ability to estimate it and the error margins around it.
However, what I want to request is that we look at the
biological significance of that temperature change. We look at the
variation seasonally. I don't know how closely you can model it. At
least a monthly basis, in some times of the year it would be important
to look at that on a weekly basis.
And then the other point I would like to make is that it would
be -- it is fantastic to have you here in person in January. Because I
know how hard it is to give a presentation over the phone when
you're staring at your own computer and you have a telephone and
we'd love to see you if we can. Thanks.
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MR. PADULA: No need to respond.
MS. WALKER: The point is I would like to see the biological
significance of that temperature change used. We need to know why
that makes a difference, if it does, and it may.
MR. PADULA: Thanks.
Any other questions?
Okay. Thank you, John. We are going to --
MR. HAMRICK: Well, thank you for bearing with me over
the phone here. As I said, I'll be happy to respond to, you know, the
rest of the commentary.
MR. PADULA: Perfect. Thank you.
We move on to Mercury and that's Harry's and Rob
(indiscernible), and then we will have a break after this one.
MERCURY ASSESSMENT AND POTENTIAL FOR
BIOACCUMULATION (STUDY 5.7)
MR. GIBBONS: Okay. Mercury study was put together so
we could help understand the fate and nature of mercury within the
reservoir and the watershed. And so we wanted to understand how
it's available, what its sources were, and how it was with different
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matrixes within the system. So we want to understand where it was
in terms of water -- flow water and sediment, the sediment itself,
how that translated to the current biological availability and the
current accumulation of the food chains, so we're looking at different
elements within that system and trying to map where are there
potential soil and vegetation organics that would lead in the
inundation area that would lead to increase in metalization of
mercury (indiscernible) accumulation potential. So, and that's kind
of an overview of what we were looking for.
A had -- let's move on to key one here.
A few variances in what we had to do. We had some study
locations that had to be fine-tuned it a little bit because of access
issues. We had trouble getting to them in terms of location so that it
seems like variation but still sampling the same reach representative -
- representative reach, so that was important.
There were also with three of the areas, a slight modification
in terms of how we were able to take the sediment and the pooled
water because of, again, how do you get valid samples.
We had to change the approach that was in our study plan in
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terms of how we were going to gather the sediment from a classical
(indiscernible) than the type of ground sample to a stainless steel
(indiscernible).
Also in some of the terrestrial samples, we had some
(indiscernible), so we had slight modification but within the EPA
guideline in order to extract, digest the samples essentially before we
extracted the mercury (indiscernible), so we had a representative of
that.
Some other --
MR. PADULA: Closer.
MR. GIBBONS: A little more, sorry. Closer. How's that?
We also had several species that we wanted to collect samples
from and collect a number of samples, seven to ten samples per
species. There were three species that we had to -- difficult because
of rareness and access to get them. But we didn't sample and we
added the one species in lieu of that that was up there so that we
could get that sample and (indiscernible) fish tissue samples to get a
mercury estimate there.
There were some other little variations in terms of some of the
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identification of the fish and things, but in terms of mercury, we
think we have a handle on what's kind of representative is up there
moving forward.
Some of the results, we were able to, as I said, collect soil and
vegetation samples. We have -- we are currently together our soil
and vegetation inundation area map, so we'll have that information.
We have the baseline water quality samples that we've taken a lot of
including seven focus area.
We have sediment pore water from ten locations that have
been sampled, and only four of those are (indiscernible) because of
the 2013 versus 2014
And we have collected, like I said, some fish tissue samples.
Okay. Some of the modifications that we discussed earlier
(indiscernible) included total mercury for our water quality samples.
We found that our total mercury, we didn't have as much confidence
in as we'd like to have, in terms of conducting a QA/QC assessment
of that native so we retook samples in 2014 to -- along with other
perimeters that are listed here and what -- address that issue.
And again, (indiscernible) water and sediment collection
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samples in 2013, we weren't able to access on the four to ten sites but
we have access to them now. So we got that put together and I
already mentioned some of the fish species.
We added the round whitefish and (indiscernible) whitefish
and did not -- weren't able to (indiscernible) rainbow and
(indiscernible).
For some of our manual species, we had difficulty in sampling
because of the rareness of the river otter and (indiscernible) but we
were able to obtain some samples and do have those now, and we
also (indiscernible). Where we have not been able to meet the
original study plan was in our sampling of birds. We have not
collected any bird samples for several reasons. One, the rarity of the
target birds (indiscernible) that the (indiscernible) are in and are --
we didn't want to just, you know, put them at stress because they are
stressed and rare in that area and the difficulty of actually getting
ahold of a nest or bird access for those species to get them, and so
that is a modification that we still haven't completed yet, and we're
looking at that in terms of whether or not we will need to collect the
feather samples from our (indiscernible) birds, because we'll have to
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assess (indiscernible) to see what is bioaccumulation based on what
is the increase of methylation because of the reservoir to see whether
or not that's going to add to our understanding of the
bioaccumulation (indiscernible).
Questions?
MS. VERBRUGGE: The Fish & Wildlife Service thinks it's
extremely important to actually get bio monitoring data, to get the
actual fur, feather, or even blood if its feathers aren't (indiscernible)
We want actual data. We do not think that pathway analysis and
literature review or modeling are sufficient.
We need actual numbers in order to understand the baseline
and to determine if there's any (indiscernible) capacity for additional
mercury exposure or whether they're already, you know, added at a
level of risk because with the levels that they have right now, we
need that information for our decision-making. And that is in the
(indiscernible) study, and we want it to stay there. [It’s extremely
important to get bird feathers or eagle blood. We want actual data
we need numbers; pathways and literature review is not sufficient to
determine if there is assimilative capacity for additional exposure.
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We want that as part of our study.]
MR. PADULA: Thank you.
MR. CONDER: Hi. Jason Conder with Environ. I have a few
questions. I'll just kind of go through my list here.
[Can you talk more about the pathways analysis? Are these
figures or numerical models- what number comes out the other end?
Are you comparing to toxicity reference loads? Are those numbers?
Continue to refine and be explicit as you can what can come out of
the other end of the model? You have a lot of great ingredients but
I’m not sure what you’re baking at the end of the day? What are the
ingredients? We want to be able to evaluate the parameters.]
MR. GIBBONS: Okay. Here's the pathways that we
presented before. Of the (indiscernible), we're basically going to
have three different pathways (indiscernible) models that we're going
to develop.
One is the (indiscernible) model, what's happening
(indiscernible) in terms of methylation of going through the system.
The others and the (indiscernible) that I have up here, the mature
reservoir. In other words, after a while we'll be (indiscernible)
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degradable that could be the methylation and that's going to diminish
over time. Sand sedimentation and stuff, we anticipate there is going
to be a different dynamic in terms of methylation when the
(indiscernible) first occurs through a period of years. We're trying
figure out with all the others and figure out how long it's going to be.
But then there's -- once the stabilization period comes, then there's
(indiscernible) and that's what this represents. So we're looking at
that.
But what I don't have here but is in other tech memos and
things that (indiscernible) is what are we really looking at. We're
looking at what is waterfall conditions and what is the organic load,
and what the (indiscernible) condition. In other words, is it
(indiscernible) condition and what is the source of mercury there and
those combos to set up what those combination of things could lead
to methylation and then how would that fit into this pathway to
where we have (indiscernible) based on (indiscernible) chemical and
biological condition of the reservoir and the (indiscernible).
MR. CONDER: So are they figures? Are they numerical
models? [Are there 30 ppm in fur? Can you quantify that? Is there
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mercury in sediment?]
MR. GIBBONS: It's a combo of both.
MR. CONDER: Okay. What number comes out the other
end? You field all this great data and model assumptions and you
have some built-in (indiscernible), but what's the numbers? Is it a
hazard quotation or are you comparing to toxicity reference values or
just going to be mercury loads or what's going to come out the other
end?
MR. GIBBONS: Good question. One of the things that's
going to come out is we'll use this to work with the three
(indiscernible) models for reservoir to help make sure we have a
realistic prediction of what's going to occur in the reservoir for water
quality and predicting actual methylation that becomes available and
so if you look at our existing condition, look at what -- if there's an
increase, how much of an increase , how that's going to move
through the system based on different uptake abilities and paths that
they can occur and then help quantify that as much as possible
though that (indiscernible).
MR. CONDER: So the numbers are going to be predicted
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concentrations in wildlife or --
MR. GIBBONS: First (indiscernible - distance from
microphone).
MR. CONDER: I'm still not exactly sure what's missing.
MR. GIBBONS: (Indiscernible - distance from microphone)
from that, where are we at with the existing condition today, and then
we can use and go beyond that -- in terms of estimating and quantify
at this point.
MR. CONDER: Right, right. Okay. And the problem is, I'm
still trying to kind of figure out what's going on, because I'm the
ecological risk assessor, so I usually deal in terms of hazard quotients
and comparing concentrations of (indiscernible), especially for
mercury. I do a lot of mercury risk assessment.
There's always a pathway. So I see a lot of these comments
and statements about, you know, since the potential for pathways.
And your figure there is great, you know, it captures a lot of what's
going on. And obviously there are pathways, for sure, and there will
be pathways after a reservoir is built and there are pathways now.
The fish are getting eaten by something out there.
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So I guess my thought is, is if you can continue to try to refine
exactly -- and be as explicit as you can, what is coming out the other
end of these models. Because all the data you guys are collecting is
great. You have fish livers and fish fillets and sediment and water
and all this great stuff. You know, you have a lot of great
ingredients, but I'm not still quite sure what you're baking at the end
of the day. Is it -- are we baking cookies or a cake, or is it lasagna?
Do we need more glacial flour, you know, what are we working with
here?
So okay. It's good to hear. So again, try to, if we can, let's try
to get a little more explicit with what we're baking here. [I have a
note about correction factor for the water samples. Can you talk
more about that? I echo earlier comments on 5.5 that we need to see
lab data validation reports. We need to see data and bird data.
Specifically getting blood from eagles. It sounded as if the agencies
were on board with the concept and then it was not implemented but
we spoke about it at one of the technical work group meetings. You
are requesting a modification to drop this data. We would like to
modify the study and get bird blood instead. It is in the RSP. ]
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MS. VERBRUGGE: And also what the ingredients are,
because we want to be able to evaluate the difference parameters and
how your parameters are accessing it and, you know, to evaluate that
market as well, not just the (indiscernible)
MR. GIBBONS: Right. That's what we're trying to go from.
MS. VERBRUGGE: And I had a question for you about -- I
can't remember where I saw it, it was in one of those -- one of the
(indiscernible) slides, you didn't show it today. But somewhere I saw
something about something about 30 part per million in fur. Can you
tell me what that sample was and -- am I remembering that right?
MR. GIBBONS: Slide 8 maybe.
MS. VERBRUGGE: Did you have fur results, and what did
they come from and what were they?
MR. GIBBONS: Yes, we had some fur results. Had some
otter and a couple of (indiscernible.)
MS. VERBRUGGE: I can't read that. Can you read that?
MR. GIBBONS: Slide 8 maybe at the bottom.
So this is kind of the range, a minimum and maximum we had.
I will qualify that some of our maxes all represent a small number of
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samples. For instance, on some of them, represent small fur samples.
So like the mercury in sediment, for instance, that was a relatively
small number compared to the whole data. It was more down in the
lower number. We didn't have much -- many samples for fur.
MS. VERBRUGGE: How many did you have?
MR. GIBBONS: I'd have to check on it. Maybe I only had
one CR -- I mean one (indiscernible.) Four maybe
MR. DWORIAN: I know the answer. We had two river otter
samples and two minks.
MR. GIBBONS: Okay.
MR. DWORIAN: One of the river otter samples was from
(indiscernible) in the study area and I think the full volume of
samples (indiscernible) but we still managed to analyze it and get
results.
The mink -- the two mink and the other river otter sample were
-- they're an Alaskan story, but we found a trapper who had trapped
them nearby and we trapped two mink and river otter and so we
purchased those furs and analyzed those. So we had two otters and
two minks.
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And while we're on this slide, there's a note about the
correction factor for all those water samples. Can you talk a little bit
more about that?
MR. GIBBONS: The total mercury (indiscernible) in the
white columns was QA/QC from (indiscernible) total mercury
(indiscernible) --
MR. PADULA: Speak up a little.
MR. GIBBONS: Total mercury in 2013 we weren't satisfied
with the QA/QC assessment, and that's why we're retaking total
mercury in 2/14 but currently doing the QA/QC analysis for the 2014
data, and we will see if we can find the correction data to broaden
our data base to use the 2013 data. If we can't, we're just going to
(indiscernible).
MR. CONDER: Okay. And I guess, you know, I'd echo our
earlier comments on 5.5, where if we can see a really nice write-up
of walking through that data, walking through those correction
factors, because again we want to get to an understanding of the data
beyond just looking at it in the database.
MR. GIBBONS: Absolutely.
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MS. VERBRUGGE: I guess I will say that the result of the
(indiscernible), it really points out the need that we actually do need
this data. Because that's a pretty (indiscernible) high number,
actually, and so we need this data and we need it for (indiscernible).
And I know we discussed in an earlier (indiscernible) that
maybe it would make more sense to get blood from nestlings. And
I'd like to know where that idea, you know, went. Are we still
thinking about that? Because I think it would be, you know, a really
important thing to do, if you can do it.
MR. PADULA: Is Brian on the phone? Brian, are you on the
phone?
BRIAN: Yes, but I couldn't hear the question.
MR. GIBBONS: So I think the question was related to
sampling of the avian population, specifically getting blood from
eagles to test for mercury. Can you address that a bit in terms of
what that would entail?
MS. VERBRUGGE: Well, we had talked about doing that at a
technical working group meeting, and it sounded like the agencies
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were on board and -- with the concept and -- but then it was not
implemented, and I was wondering, you know, whether it will be, is
it still on the table, because, you know, at one of the technical
working group meetings it seemed like a real possibility.
MR. GIBBONS: The decision I think, and then Brian can get
into the details, if you want details, I think the decision is still one
we're going to try and actively make that determination. You made a
comment that you want to see the data and we're still assessing how
much value that is so that's a thing to be discussed. It's not off the
table. It's not currently on right now.
MS. VERBRUGGE: I guess you're requesting a modification
to drop this this biomonitoring data. I'm making the suggestion to
modify the study in another way, that instead of getting feathers that
we also get blood as we discussed, so it's just two different
modifications that we're discussing (indiscernible). [When will AEA
make that decision whether or not they are going to ask for a
modification.- This will be discussed in January to see what we all
concur.]
MS. MCGREGOR: This is Betsy with AEA. I think I can
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clarify that for you. We are right now trying to consider whether or
not we need that data. If we do need that data, then we are going
with the method that we had discussed in the March (indiscernible)
record meetings.
MS. VERBRUGGE: It's in the FERC-approved study plan
though that you need that data.
MS. MCGREGOR: But the methodology that you were
discussing that we change from the blood and feathers that we
discussed in the March meeting; that the way that we would proceed.
So right now it's a proposed modification where I think it's a decision
point whether or not we actually need the data. That's our stance at
this point in time. If you're putting in as a proposed month or I guess
FERC does a statement determination of whether or not they accept
the proposal modification, we put in proposed modifications to stay
with the existing SRP and collect that data, we would collect it in the
methods that we discussed in March.
MS. LANCE: Ellen Lance, Fish & Wildlife Service. So when
will the AEA make that decision whether or not they're going to ask
for a modification?
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MR. GIBBONS: I think that's going to be after our January
meetings; is that correct?
MS. MCCRACKEN: Right now it's (indiscernible) proposed
(indiscernible) modification.
MR. GIBBONS: Oh, modification. I'm sorry.
MS. MCCRACKEN: And then it's up to what you come up
with the pathway and the analysis and the data.
MR. GIBBONS: So that will be discussed in January to see
what we all concur?
MS. MCCRACKEN: Right.
MR. PADULA: Any questions on the study?
MS. LONG: I have a question about -- you mentioned -- well,
two more questions. Stabilization of the reservoir when
(indiscernible) mercury will not be created or whatever it is, I'm not
an expert in this, approximately how many years and then my second
part of that question is -- so to get into the stabilization time of the
reservoir and it doesn't matter if the level of water in the
(indiscernible) zone goes up and down, that doesn't affect it after we
get into the stabilization (indiscernible) or whether (indiscernible)
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mercury is created. Thank you. [Will there be stabilization of the
reservoir when methyl mercury will not be created obtained from the
literature review? In approximately how many years will this
happen? Describe the stabilization time of the reservoir? So, it
doesn’t matter if water level goes up and down whether or not
methylmercury is created?]
MR. PADULA: That was Becky Long.
MR. GIBBONS: Okay, there's multiple parts that I will try to
cover. First, methylation of mercury (indiscernible) is occurring
now. That's how part of this getting into the (indiscernible). And
when I mentioned a mature reservoir, I'm talking about the
methylation based on your (indiscernible) that are integrated based
on inundation that occurs now and that degradation of that one. This
mature reservoir model will take into effect both the production that
comes in from (indiscernible) and the production that's generated
within the reservoir in terms of organics. Also it will be looking at in
a general way because we don't have absolute data on other sources.
We're looking at the geological sources we also have [indiscernible]
sources we have to access in their stable environment whether that
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source is going to increase the source of mercury or not and whether
that mercury source itself has the conditions in the reservoir that
needs leads to the increased methylation such as load dissolve
oxygen and (indiscernible) or can the reservoir be such that those
conditions are not going to be present to enhance that methylation.
Okay? So that's kind of what we're trying to look at.
MS. NOLAND: This is Laura Noland with Environ. On Slide
14, you made the statement that AEA is not proposing any additional
sampling for mercury until 2015. But based on the discussion on
theories of discussion, you still have not evaluated the data for 2014.
So, I'm wondering how you can make that decision. [You make a
statement that AEA is not proposing any additional sampling for
mercury in 2014, but based on discussion you still have not evaluated
this data so how did you make that decision? You think you have
sufficient data? But you don’t really know yet?]
MR. GIBBONS: Not all of the data would go into it but a lot
of the data. In the mercury study, remember we're looking at the
different compounds of (indiscernible) that we're still debating
whether to do (indiscernible) of course. The water quality has
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already been taken and we're evaluating (indiscernible) but we think
we'll have valid data there so we can move forward.
MS. NOLAND: Well, I guess that's the point. You think you
(indiscernible) but you don't really know yet. I mean, that's what I'm
trying to get at.
MR. PADULA: All right. Anything else for Harry? Okay.
Let's take a ten-minute break, and we'll wrap up the day with the
groundwater study.
(off record.)
GROUNDWATER (STUDY 7.5)
MR. LILLY: We'll get started in 30 seconds or sooner. So, I
think I will go ahead and get started. It looks like most people are
back in the room and sitting down and so I'm the study lead for the
Groundwater Study 7.5.
In the groundwater study, previously had a very long name and
it's really groundwater surface water interactions we're looking at. A
lot of multi-study components particularly with aquatic and
occurring resources, so I'll cover on that today.
And also given the prior studies that everybody has reviewed,
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these presentations, so I'll go through all the slides, and then we can
get back to any of the slides to specific questions.
In the objectives, to not read all of this off, but I think
assuming everybody has looked at this, clearly about summarizing
what information existed before in the '80s, what has existed in
studies in, other Arctic regions. What are the large scale
(indiscernible) information processes that we have to know to help us
understand really what's going on in a smaller scale, aquatic and
riparian resource areas.
And then also how this ground -- you know, how does
potential project affects impact shallow groundwater users.
And we look at this not only in summer, but really through all
the major four hydrologic seasons of the year, which includes
break-up, winter, the ice freeze-up process in the fall and summer.
So it's looking at it year round.
The study components really line up with that previous slide,
so if you look at the objectives, the components are directly in line
with that.
And then in terms of variances, the only thing I wanted to say
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here, is all these variances were only variances in schedule, and
we -- because of the amount of effort taking place, but getting all the
-- particularly data infrastructure in place in 2013, mostly variances
are all things that were shifted back in time for those elements that
could be shifted back.
An example talked about earlier today was like in the
bibliography work. It's not that we weren't looking at the literature
of the '80s and everything up front because we were, but it's a point
of completion that's pushed back so we could both includes more
information and deal with the priorities that we had particularly in a
very intense field program in 2013.
For the summary of results in the ISR, again, we focused on
five major focus area investigations. There were 57 hydrology
stations installed, 66 wells were installed following the same kind of
method used in the '80s. That was talked about in prior
(indiscernible) meetings. A lot of the empirical data collected over
these four major hydrologic parts of the (indiscernible) cycle.
Some of the key real observations was the presence of shallow
groundwater, which was a real key observation that you'll see in
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components of the ISR and also in the technical memos that were
just released, in terms of your reviews that will be taking place
between now and January. I would point that out.
The -- and then the upland and hydrologic recharge from the
river valleys really focusing on that to understand the groundwater
system and how it interacts, you really have to look at the whole
valley system and where our recharge is occurring, and that explains
the nature of the consistent shallow groundwater claim that we see.
And that we're doing this both winter and summer so there's also an
intensive point of the program with this.
In looking at the summary of results, since the ISR, we also
and kind of a lot of it was response to the November meetings that
the agencies attended where, you know, there was discussions about
how do we quantify gaining and losing reaches and doing discharge
measurements. This in 2014, there was work done in particularly
April, in the winter sampling, and you'll see this data in the TMs that
were just released. The end of -- where we did discharge
measurements at a whole number of stations, during the summer we
installed 42 staff gables to locations, where 25 of these were just
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completed. Discharge measurements for end of summer conditions,
in September, October, and that we maintain the data collection
components in the five main focus areas and added some
components to others. So now the groundwater studies looking at
seven focus areas, but the five main ones that were started in 2013
are the most intensive, so.
And then just some of the summary results and these are in the
technical memos that I think ya'll are just starting the review process
on, is showing how some of this data is used and you can see both
the 2013 and '14 data in this to look at, as an example, in looking at
response functions, and how does the lateral habitat change when we
have natural changes in our system, and how does this also change
important characteristics such as the thermal characteristics in the --
(indiscernible) spawn the areas.
These are looking at just some of the examples that are in
these technical memos that were just released, and again, this is just
looking at -- these are two examples -- we'll get down low enough on
the examples of 2013 and '14 and information.
Looking at some of the -- for the work on the riparian efforts,
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this is looking at some of the cross-sectional modeling efforts where
there were a lot of questions in the past for the groundwater study
about why this -- you know, how do we use a cross-sectional
approach to understanding but understanding the lateral hydraulic
radiance and this is just showing examples of this, which is discussed
in the ISR in the following technical memos.
Same in this area where we're looking at how do we use this
(indiscernible) information and profile studies.
The -- so for the proposed modifications, this again was
something that was just scheduled to line us up with other studies
and was a change in schedules, there's no change in the data
collection components or their objectives.
The new modifications really are just the same thing, but
they're just changes in the schedule. Task being completed in 2014
where ongoing data collection efforts (indiscernible) part of that, and
the steps to complete the study as described in the study plans.
MR. PADULA: Nice job.
MR. LILLY: I think that breaks my record for the fastest
presentation.
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MR. FULLERTON: You shattered my 12.
MR. LILLY: So with that, I'd be happy to answer any
questions.
MR. MUNTER: Yes. Is this on? All right. I'm not a
technologist here, so.
My name is Jim Munter, J.A. Munter Consulting. I'm also
new on the project, so I'm still scratching my head over a few things
here.
But, you know, the study plan called for upscaling results to
these focus areas. How are you going to do that?
MR. LILLY: That's a good question, Jim. And I think if you
get into your review of the technical memos that were released, I'd
point out particularly to the task (indiscernible) related to our riparian
studies. And this is how we look at these cross-sectional gradients
that we've particularly chosen (indiscernible) outside focus areas, to
say what are the components we noticed in the landscape that are
indications of shallow groundwater that would allow us to take the
available information outside of those focus areas such as the DM
?information that is being collected by geomorphology studies and
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information such as (indiscernible) riparian and vegetation studies
where we're looking at the presence of vegetation cover that indicate
shallow groundwater and come up with mapping layers for looking
out. What are the shallow groundwater occurrences that we see
along the valley and in the uplands habitat that will bound the system
so we come up with an idea of the consistent -- the nature and
consistency of that, and this fits into the detailed studies of the focus
areas and then methods of transferring those outside the riparian
scale so I --
MR. MUNTER: That's a very good summary. Thank you, but
earlier we talked about the thermal IR imagery not being collected
for these focus areas, and I'd like you to comment on how useful the
thermal IR imagery is to this upscaling and baseline analysis.
MR. LILLY: Well, on the thermal imagery, when it was
initially -- there was thermal imagery collected in 2012. Then -- but
there was additional thermal imagery collected in the focus areas and
tributaries and at a finer resolution and more coordination with our
current data collection efforts at the end of 2013, and so there was
thermal imagery collected, so I reference you to that information.
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MR. MUNTER: Okay. Maybe I just didn't understand then
how much imagery is out there.
Well, with regard to variances, I didn't see any reference in the
ISR to nested piezometers to define vertical groundwater radiance
which was part of the study plan. You know, 66 piezometers or
wells put in. It looks like they're all in different places, but they're
not nested at the same spot to get different water levels at different
depths. Can you comment on that, please?
MR. LILLY: You bet. So for the wells in the main
configuration of the wells, we're to look in terms of the internal
boundary conditions and at different distances away from sloughs or
side channels and habitats, look at pressure responses through that.
In looking at the nature of shallow groundwater system and
where we had -- you know, was there a need to have wells at depth
and we determined we did not really need to have that if we could
look at the groundwater conditions from the upland areas all the way
down into -- when I say upland, I mean at the base of major hill
slopes down to the river itself along the way.
MR. MUNTER: Okay. I see your point; that the vertical
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gradients might not be too important, but I think it should be noted as
a variance because it was called for in the site plan.
And then that leads into my next question, has to do with the
modeling effort. That the presumption going into the study plan of
these transit models is that they would be oriented parallel to the
direction of groundwater flow. Typically that's how those things
work. You get water going in one side, flowing along the flowline,
and then coming out or being discharged by well or whatever.
I mean, physically, these things are kind of like ant farms, with
glass plates on each side. And as the data has come out and I've
looked at it, it strikes me that these flow systems are actually
complicated three-dimensional flow systems that vary dramatically at
times. They are four dimensional. And I notice in the (indiscernible)
study area, you've proposed to do some three-dimensional modeling,
which I think will help unravel that.
One of the ways to get a handle on this, and I'm surprised I'm
not seeing it in your work so far, is a series of water-table maps. You
have in some areas lots of data that will facilitate construction of a
water-table map that would document what these groundwater flow
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systems look like and allow a determination of groundwater flow
direction and allow an evaluation of whether or not these transects
are located in a technically valid orientation to do that kind of pulse
and response modeling that you're referring to.
So I guess there's several questions buried in there. One is, are
you planning on doing any water-table maps to illustrate the
dynamics of the groundwater flow system?
MR. LILLY: Yes, and we've worked on that.
MR. MUNTER: Okay. And I would assume then that you'll
look at the orientation of these transects with regard to those
water-table maps.
And I what I would like to toss out here today, is to consider
evaluating two-dimensional plan-view groundwater-flow modeling
to do the kind of simulations that you're looking to. I think it could
potentially work. It's not part of your study plan, but it may be a
better mechanism for capturing the dynamics that you're seeing and
in the pulses that you're seeing, and it would solve this problem of
what direction groundwater is flowing.
And one of the reasons for this is that all your data is really in
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the horizontal plane. You don't have data at depths with these
vertical groundwater gradients, and that's usually what the main thing
is, the transect model is trying to simulate and calibrate to, is that
deeper groundwater flow data, and since the data is not there, it's not
particularly important. I think that the data you've collected would
argue towards reevaluating this approach.
MR. LILLY: But, Jim, let me -- so if I was only modeling
groundwater to only understanding groundwater, it would be a little
bit more component of that. But one of the objectives, and I want to
talk about two, we are drilling cross-sectional groundwater models
for two separate purposes.
One for riparian, so where we chose the riparian transects
needed to line up with where we had certain types of riparian
vegetative cover. And we wanted to make sure that we had a good
representation of different types of vegetative systems, but also in
relationship to hydrologic boundaries and different water-table
elevations; so all that went into the selection that you see in those.
And I think that, you know, -- so in terms of moving them
around, there's an optimization, not just on the hydrology, but on the
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land cover itself.
And then on the second side, the other transects were
identified by -- in the '80s, where they identified key aquatic habitat,
particularly for small (indiscernible) who sat down with IFS
(indiscernible) ground and did find where these areas would really
need to use models as a way to understand groundwater/surface
water interaction processes, which is the primary purpose. But we
wanted to place those where the information is most useful to the IFS
and fishermen crew.
MR. MUNTER: Well, I can see those objectives. I've done
2D modeling and 3D modeling, cross-section plant view of surface
water bodies and we'll incorporate those surface water bodies and I
think probably achieve those objectives.
And one of the advantages is, yes, part of your upscaling is to
take the results of your focus area analysis and translate it to a bigger
area and you're going to have a variety of habitats and riparian?
vegetation and if you have a plant view model, you get much greater
coverage of different habitats seeing what happens with different
water levels up or down. And actually it might be a better approach
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to achieving the objective of relating the water level fluctuations and
the pulses to the large surface area of habitat and vegetation cover
out there.
MR. LILLY: Those are good points, and that's why
(indiscernible) are still a focus area, to help look at what are the
differences we have between looking at the system only and we're
not -- we're looking at the hydrology of the system, but the whole
focus area scale, but modeling where we have those intense transects,
where we're doing that modeling of those transects in that
two-dimensional profile that you mentioned.
But it doesn't mean we're not looking at hydrology of the
whole area. But slough slide A was chosen as a place for them to
look at, but what is the effect of only looking at a few of these
transects and how this three-dimensional nature of the (indiscernible)
play into it.
So those thoughts that you just said were fundamental then to
choosing slough (indiscernible) A as an example that we put
(indiscernible.)
MR. MUNTER: Our related concept --
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MR. RUSSO: Michael? Hi, Michael, this is Tim Russo
(indiscernible) first contacting and I have a few questions, too,
related to what was just asked about the work (indiscernible)
characterize the groundwork (indiscernible) particularly the structure
of the (indiscernible.) Were you going to do the (indiscernible)
model. What steps are the (indiscernible) and those words that are
constructed? And what types of hydro geologic units are they in?
Are they in sand or silt?
Do you have any idea of what degree of (indiscernible) is in
those areas? And (indiscernible) have you been able to tie any of this
data into more useful data that may be available in study plans?
Really why I'm asking, I understand -- I think I understand what
your plan is, that you're going to (indiscernible) hydrologic cross data
that's been collected and (indiscernible) and you've got a lot of that
data now.
But I'm wondering how it's going to be useful without putting
into the context (indiscernible). And my major concern is that the
models won't be set up properly to give meaningful results, which I
know that's your concern as well.
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But basically I'm wondering how things are being set up right
now to adequately represent that hydro geological framework in
terms of the morphology (indiscernible) units, the boundaries
(indiscernible) and other things.
I realize that I may be jumping the gun on some of these
things, but we're pretty far down the road now and there's still
nothing presented as far as I've seen as to subsurface concept models
where the hydrological framework, these are usually the first tests
that we do at any (indiscernible.) It was my understanding from the
study plan, this was to be done 2013. Could you comment on that?
MR. LILLY: Sure. You had a couple of comments there.
The -- so the geohydrology, the framework, the information that's
coming out of the geomorphology studies, as was discussed earlier
today, is being used, and it was going to be beneficial to see them
complete the geomorphology mapping, because that was going to be
one of the inputs that we were using in the geologic framework so
the depths of -- that information was all being collected last year and
is being put together. And some of the cross-sectional information
on that is in the TMs that were just put out, that, you know,
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meteorologists is going to be starting the new process zone so I won't
talk too much about that unless you want to go into it.
The -- for the wells, in the depth of wells, they were all done in
similar methods, done in the '80's, where we used drive point
methods. These are hard to access areas, and it's -- so we used a
combination of drilling and drive methods, so we're monitoring
really the top of the water table, which was, for what we were after,
was -- particularly for both riparian and aquatic, what are the
boundary conditions and how they are changing? This is the main
information we were after, was the top of the water because we're
really dealing with the water-table configuration.
We also noticed that in many of these areas, we had -- we
didn't even need to drill wells in some areas because we had lots of
springs seeps and wetlands where the water table is intersecting the
land surface. So our groundwater information is not only coming
from the wells, but it's coming from many of the other features we
see that give us indications that we have very shallow groundwater
systems in the area. And even our aerial flights, we have aerial
photographs, we're using that information because all of that is
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telling us something about the groundwater conditions.
If we had deep groundwater systems, we wouldn't be able to
do that. But one of the things that we've seen consistently in the
middle river is that we have shallow ground water systems in the
uplands and in the areas of the lateral habitat in many of those places.
And I don't think I answered all of your -- you had a number of
statements and questions, but I think it was pulling all of this
information together so that we can develop the continuing
development of the geohydrologic models and then come up with the
flow models, which are to really help us with process and understand
it.
And, Jim, one of the things you mentioned was, you know,
there are times you do cross-sectional models along flow lines. But
we purposely are not doing cross flow lines. We are trying to be
perpendicular from the sources of stress, which is the river.
So what we're looking at in terms of, just like using a river as a
pump test, and you have wells going out in different directions away
from your source of the hydrologic stress, is that's why we have the
orientation of the transects as they are. And that's been done in other
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areas. So I think I answered two questions --
MR. RUSSO: Because (indiscernible - interference with
speaker-phone) since whenever (indiscernible) models in the
direction of out groundwater flow, there are going to be some errors
in terms of the flow that's predicted (indiscernible). And I'm
wondering how you're going to qualify that.
And I know on the Chena River you did do it 2D horizontal
models that quantify those areas, and I don't see anything composed
in that here.
MR. LILLY: Well, that's why we proposed the
three-dimensional modeling in FA 128 or (indiscernible) so that we
could look at the effect of the two-dimensional assumption
associated with the transect models. Very similar to what we did on
the Chena.
MR. MUNTER: This is Jim Munter again. To weigh into that
discussion. My concern here is that the flow systems are changing so
rapidly that those adjustments may be very difficult and inaccurate.
In other words, when you start out at a flow water situation without a
pulse, you might have groundwater flowing left to right or right to
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left, and then the river jumps out, suddenly the flow direction
basically turns 90 degrees in a transient manner.
And the process of that turning of the groundwater flow
system and that pulse lining up so that your transect is properly
aligned and that is the direction of flow is -- well, I can't imagine
how you do an adjustment for that. I mean, it seems very complex,
and I haven't seen a lot of literature.
I did see the report of the Chena River that addressed that, and
the details of that 2D model and that correction factor wasn't entirely
clear to me.
So that's it. But I had another comment, I guess, if I could. I
honestly wanted to add something to what I just said that there.
MR. LILLY: Well, Jim, those are good points to bring up,
because that helps give us input on the issues that we need to look at
and those questions will be used in the data collections, so.
MR. MUNTER: Sure, okay. Thank you. I think one of the
big issues that I didn't see written up explicitly, but it's kind of in
your concept and I wanted to address it quickly here, is that we've
got a big basin, a big groundwater basin with lots of groundwater
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being recharged throughout the entire basin.
And then most of that groundwater eventually wants to go to
the ocean as expeditiously as possible, and the quickest route is to
discard to the Susitna River and its near tributaries because its
tributaries and sloughs (indiscernible.) So I'm not surprised that, you
know, you're seeing a lot of groundwater upwelling because it's hard
to get data on those deeper systems. I think it's important to do some
kind of analysis that considers that they really are there, maybe a big
picture water budget type exercise and say, well, how much
groundwater should we be discharging based on studies in other
areas. I think that would be a very valid way to look at this.
And where it gets to is understanding better these processes
that are going on in the river bottoms and you had a little write-up on
down welling and I looked at that in some detail. And I could see the
temperature data that you had that indicated that the shallow
groundwater was indeed getting colder with the onset of winter.
But typically in those environments, you want to have a
measured download hydraulic radiant that confirms that you have
down welling. And when I looked at the data that was presented on
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that slide in the nearby monitoring well and the slough, what I saw
was either upward gradients or a flat gradient, no gradient. It seems
like an odd thing. You have any explanation for what you think is
going on there?
MR. LILLY: There's a lot of variables. From -- if you're
talking about where we had the temperature profiles, where we're
looking at the thermal profiles through the bed versus the wells that
are adjacent to it, we're just seeing variation across that system. And
so that's something that's with the data that we're collecting now and
putting that information together, we're going to -- we have a lot of
variability associated with, well, where are you on the slough system,
three dimensionally, as you mentioned. So that's something that all
the data collection was intended to help answer those questions, and I
think we're headed in the right direction.
MR. MUNTER: Okay. Thank you. That helps.
MR. LILLY: You made another point about how do we
understand the groundwater contributions at the larger scale.
If you're referring back to the IFS ISR and if you look at the
winter gauging program in that, there is a whole series of
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measurements that were being conducted in cooperation with USGS.
So we're also looking at what are the gains that we've had,
particularly in state locations along the middle river, and does that
make sense to put in the regional hydrology system.
So we are seeing the evidence. This is some of the
information that Dave Brailey is collecting where we are seeing the
increase in flow through the winter measurement program where we
don't have all the other (indiscernible) in the system, with glacial
runoff and precipitation, et cetera.
MR. MUNTER: That's excellent. Thank you. That is a big
part of that puzzle, so I'm glad to hear that's working out okay.
But what I get back to with the ground welling is it surprises
me that there's much, if any, down well -- down welling in the
Susitna River bottomlands during low-flow conditions. You can get
it during temporary stage increases. You get a lot of bank storage
and water going in and out and a lot of complexity there.
But at low flow, I guess I would encourage you to, if you're
seeing evidence of down-welling, it should really be accompanied by
some clear hydraulic gradients from the monitoring wells that says,
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yes, this is, in fact, happening as an important process because then
that -- that drives your upscaling and your generalization on how --
what processes are going on and how important are they based basin-
wide.
So I think that data and that analysis is really very important to
that. So that's -- I didn't have a question. I just wanted to toss that in
here.
MR. LILLY: Well, and I think you're in a state, other
examples of where we do see down-welling. It is natural. And a lot
of what I expect us to unravel, to continue to do all this work, is
when we look at the geometric configurations of what is the
hydrologic slope, what are the nature of the bottom of the stream
channels or slough channels or tributary mouths, we're getting
localized effects where you get down lowing. You may have down
lowing right at the mouth of let's say tributary channels, where all of
a sudden your lower boundary condition in the river dropped a lot,
so now your stream bed is locally -- it's flowing through that stream
mouth. Here's a hydraulic gradient, it's moving downward.
But if we go up 1,000 feet, it's a discharge area, you're gaining
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flow. So a lot of it has to do with the relative boundary conditions.
All good questions. Is there anything else I can answer?
MR. MUNTER: It's -- one of the things that's not clear to me,
maybe partly because of my recent introduction to the project, but is
how your groundwater model results will feed into the riparian
aquatic-habitat studies. So what output from the groundwater
models specifically will feed into those other analyses, how do they -
- can you kind of flesh out how that's going to work a little bit?
MR. LILLY: Sure. For the breakup first with the riparian. So
with the -- for the riparian study, we're really looking at what is the
dependency of riparian vegetation on shallow groundwater and
where are the water budgets and so when we look at the root zone,
how much dependency do we have on shallow groundwater versus
precipitation coming in? This is why some of the work that Kevin
(indiscernible) is going to be doing and maybe covering tomorrow,
isotope work and we're looking at what are the different water
balances that the vegetation is depending on. It's very (indiscernible)
where you've had hydro power investigations that are seen, but
there's a dependency on shallow groundwater, if you change that
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groundwater configuration and change the depth, then there's
immediate impact. We have a lot of precip available in this area, so
what's the dependency of the vegetation on the precip (indiscernible)
water that's coming in through surface drainage, if there's snow melt
or summer rainfall coming to the system.
So the groundwater modeling is to look both at what the
water -- what the processes are (indiscernible), with the ET processes
in water variability in terms of water budgets, as it relates to changes
in the depth of water that are related to changes in stage
(indiscernible).
So let me stop there in case you have a question as to
(indiscernible).
MR. MUNTER: No. Got that. Keep going. Thanks.
MR. LILLY: Okay. So for aquatic, the real intentions of the
groundwater modeling is to give us a tool to see what we can't see.
What are the groundwater/surface water interactions that are
occurring in a (indiscernible) habitat area where we have mass
exchange going on, but we have hydraulic connectivity, so we see
groundwater levels go up and down, but what's the mass interaction
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that takes place?
So it's hard with only wells or only temperature profile
information, et cetera, to understand those cause-and-effect
relationships. So in this case, we're using groundwater models in one
of their typical applications to disapprove?? our understanding of
processes, so we can then take that process understanding and
distribute that next to focus area scale, and then to say what's the
available information for segment scale and apply it to that scale.
So really it's to give us a tool to understand the processes
involved, particularly with questions relating to the (indiscernible)
habitat. A lot of that is (indiscernible).
MR. MUNTER: Okay. Thank you. And if we could move to
some winter groundwater questions real quick here.
MR. LILLY: Sure.
MR. MUNTER: You had a big spike in groundwater levels
caused by an ice-jam flooding event, and that was not river flow
dependent, it was river stage dependent.
MR. LILLY: Exactly, good point.
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MR. MUNTER: In your analysis for those other habitats, are
you going to do wintertime analysis, or are you going to do this on a
seasonal basis where you're going to really just deal with, you know,
open water conditions or -- how are you going to handle that ice-jam
type event?
MR. LILLY: That's a really excellent question. The -- so
really, as I mentioned earlier, the groundwater study is looking at all
the hydraulic periods that we have, both ice cover, which are three
different -- consider those three different seasons, the fall freeze-up
process, our full winter process, spring break-up, because of these
transitional periods, are extremely important.
And our data collection efforts were set up to continuously
monitor and try to capture that as much as possible. That's why we
were really dependent upon continuous daily acquisition systems, so
that we can capture all those periods and these time-sequence events
that we can never either safely be out in the field for or even schedule
logistically to be out to capture events. And you notice that we have
mid-winter ice-jam events that have nothing to do with increases in
discharge. It's really driven by ice processes.
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And that's where with the interaction with -- of what you'll
hear Jon Zufelt talk tomorrow (indiscernible) team is, you know,
what are the mechanisms that they are going to be modeling in terms
of their river flow routing model that deal with ice cover conditions.
We'll be taking that output for the winter periods and we'll be taking
the ice-free river flow routing model output for this summer ice flow
period.? So we're (indiscernible) using dependent.
We're only modeling, you know, efforts that are interested in
groundwater modeling, where the analysis will be from those two
models, so we're looking at the whole hydraulic year.
MR. MUNTER: Okay, good, thank you. And then there's one
item that I didn't see any reference to, and I know you're familiar
with this, people commonly use icings to identify groundwater
discharge areas. By that, I mean icings caused by groundwater
discharge, comes out freezes, and then the groundwater typically
backs up behind it.
Is that an important process in this study area, or have you
seen it, or are you -- or is it not important? I mean, I really don't
know.
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MR. LILLY: No. That's an excellent -- because particularly
in the winter and the spring, icings and lack of snow cover are two
important observations for groundwater output. And we
documented, such as the dam -- where the proposed dam site location
is and other areas where we had water coming out of the banks, and
it's icing. And we got various documentation we've shown in some
of the prior TWG presentations that are on the Susitna website. So
there's some examples of that. But we're capturing those examples
where we have water coming out in the form of springs when it's
fairly warm and it's freezing up.
We also have a lot of areas in FA-115, Slough 6A is a great
example where we had places where we had groundwater springs
that are running ice free all winter long. And we have places where
even though everywhere else we have three feet of snow cover, we
have no snow cover on the landscape. The reason we don't have that
snow cover is because it's shallow groundwater, it's warmer, it's a
heat-input into the system.
So by doing aerial surveys at the end of winter, we can identify
areas of shallow groundwater just by doing those aerial surveys.
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Because we also done on the groundwater to relate those
observations to the groundwater conditions.
MR. MUNTER: Okay. I'd like to move downriver now. All
your sites, focus areas are on the three-river confluence, and yet we
heard -- I think we are all aware that the regime, for lack of a better
word, is quite different below the Three Rivers Confluence. It's
much more of a (indiscernible).
And you know, it just strikes me that the areas that you're
studying are really not representative of that lower river area. And
I'm just wondering how you're proposing to do your -- do the upscale
groundwater work and do such a different hydro geologic regime.
MR. LILLY: So, Jim, if you go to the ISR for the riparian
section, there is going to be a reference to maps that show where
walls are at four sections in the lower river. So we do have four
sections that we're in coordination with Kevin (indiscernible) riparian
study.
That information is probably useful for a variety of studies
where there's two wells and a surface water measuring point, and
four transects that are downstream of Talkeetna. So we take those
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pretty far down, so we're covering that range. So I'll point that out.
MR. MUNTER: That's a good point. And I did notice those
in the study, but it sort of came in from the side. Because as I read
your nine objectives, it didn't seem to me that they sort of fit in any
of them and I didn't read much text about why they were there, what
they were for, how they were going to be used. I mean, it's a pretty
murky process from looking only at your report.
So maybe it's more evident as the riparians have
(indiscernible) and figure that out.
But even -- even given that those four wells are there, maybe
you can just address what you're going to do to determine the effects
of the project with regard to groundwater down that lower river area.
MR. LILLY: So the groundwater questions that we really
were given for our riparian was what's the nature of the natural
variation that we see now. So we put in -- there's four -- more than
four wells. There's four transects. And one of the transects is
actually two sets of study sites on the lower river.
So the real question that Kevin Fetherston and I talked about
was what's the depth of groundwater in the natural regime, so we can
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then look at based upon the (indiscernible) models and how they give
an indication of how it's going to change, then how well we -- what
will we -- will that change be something within the natural variability
that we see now.
So it's much -- we had simpler questions and fewer questions
down there, and it was strictly for looking at the depth of water
versus the -- what the vegetation was using.
Kevin, do you want to comment on that?
MR. FETHERSTON: Yeah. Our (Indiscernible - distance
from microphone.)
MR. FETHERSTON: I am Kevin Fetherston. I am the lead
riparian (indiscernible) study that Michael is talking about here. And
you have four transects in lower river. Our groundwater study on
there is essentially characterizing the relationship between
(indiscernible) areas and groundwater. And in addition to the
intensive studies we're doing in the middle river, the scope of the
work (indiscernible) as our current studies in the middle river.
So characterization using groundwater levels (indiscernible),
looking at the relationship between the beginning stage and
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(indiscernible) aquifer water levels, and (indiscernible) the objective
of the surface water riparian study is to look at the relationship
between (indiscernible) plant communities and groundwater capillary
(indiscernible), basically (indiscernible). And that's a picture of our
(indiscernible).
MR. MUNTER: I think I only have one more question, slash,
comment.
As I look through the data in one of the website that had
endless amounts of data, we weren't able to find well depth as one of
the parameters reported. And it could be that we just missed it, but it
could be that it was not there.
And I guess I would just encourage you to look into that,
because that would be the standard item that would be included in a
data appendix.
MR. LILLY: I'll make sure that's addressed.
MR. PADULA: Question over here from Domoni.
MS. GLASS: This is Domoni. Just a quick simple question. I
just want to know post-project flows and geomorphology change,
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are you going to be able to predict the change in groundwater
(indiscernible).
MR. LILLY: The intent with the groundwater studies is to
provide the process understanding, so that when we look at where the
post-project conditions, that we can look to see what are the changes
in (indiscernible). So yes.
MR. PADULA: Any other questions for Michael? Sue?
MS. WALKER: Yeah. Just a clarifying question relative to
Domoni's questions, and that is, I'm not sure that I understood your
answer. Will the study be able to project the project effects on
groundwater, or will you be assessing the changes to groundwater
after the project is under operation?
MR. LILLY: There's different ways of answering that
question. So let me -- by developing the understanding of the current
processes in the current system and the variability, and then looking
at when we -- under the state -- the main channel stage changes,
because it's really a stage-to-stage relationship that we're looking at
in terms of how it affects lateral habitat and (indiscernible).
But it -- the outcome of the groundwater study is to understand
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the process understanding, so that if we come up with different stage
characteristics in the main channel, we can understand how that
impacts the lateral habitat regimes, which includes the groundwater
upwelling or recharge/discharge, I guess.
MS. WALKER: Okay. That's just stage change after the
project. It's not an explicit study goal that the study will be able to
estimate or project the effects of the project on groundwater over
time.
MR. LILLY: Groundwater is a basin-wide concept, so I'd
have to say you'll want to -- you'll need to clarify that in terms of
groundwater in the lateral habitat. I think it is an effect of the study
to look to see how groundwater is impacted in terms of relationships
to riparian habitat or the work that Kevin, you know, was just talking
about, you know, in aquatic products? So I believe the answer is yes,
the objective is to understand that. And this fits into some of the --I
think you're going to hear tomorrow with IFS and some of the
aquatic habitat modeling efforts.
MS. GLASS: I'd just like a follow-up here. As a fish
biologist, see fish (indiscernible) in places where we've got
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(indiscernible) water and often that water is downwell somewhere
else, below the subsurface, the changes and characteristics when it
comes up. After the dam is put in, you're not only going to change
the stage, you're going to have a change in geomorphology. And I'm
hoping that geomorphologists are going to be able to tell us where,
you know, things are -- deposition is going to change within the
basin.
If you know where those places are, are you going to be able
to talk about where -- where we're losing or maybe gaining,
up-welling, that well supports spawning fish?
MR. LILLY: Yes. And the reason why I'm going to say yes is
that what we're -- and I would refer you to the technical memos
related to riparian habitation, because it has some very good cross
sections in it to look at the cross-section relationships between the
upland groundwater system and the river itself. And that's the
process understanding that's transferable, that as you change the -- if
the geomorphology changes take place and the changing
configuration of wild habitat, the relationship of those vertical
gradients, that understanding is what's going to allow you to then say
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how does it change up-welling or down-welling conditions.
MS. MCCRACKEN: This is Betsy McCracken with Fish &
Wildlife Service, and I need to ask a clarifying question and I
probably asked this before.
But did you do the nested piezometers at the micro-habitat
scale in focus areas? And were they co-located with a fish presence
and fish absence or any of the other studies like the water quality,
temperature, and (indiscernible) productivity?
MR. LILLY: Where the aquatic sections were done in
coordination with IFS, so those are all at key aquatic areas where
they're taking other measurements for both IFS and fish resources.
So our sections are co-located where there's other ongoing
investigations for that.
Along with the -- for the riparian side, there's a lot of
information with the riparian vegetation groups, they are also
collecting along those transects, so they're in coordination with that.
The nested piezometer approach was when we looked at
what's the information that we need to understand the water-table
configurations? We did not do nested parameters after going in to
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the study plan ? Because we felt that was not a viable approach to
take.
And by nested, what generally people are meaning is that you
have several wells at different depths. But we felt that with the
questions that we were trying to answer, that that was not necessary.
And it -- under the methods that we used to install the wells, with
dry-point methods, it also wasn't real practical technique for them.
But the main method was that we felt like we could answer the
questions by understanding where the top of the water table was and
understanding these transects because that gives us an idea. If we
only had one set of wells in one area, we would really need to have
nested wells and the fact that we had these wells along these
transects. I hope -- I feel gives us a good idea of what the larger
groundwater picture is and along that transecting, what some of the
vertical components are.
MS. MCCRACKEN: So can we find where you -- which
focus areas that you studied and did you do more than, you know,
what was the effort that you put in?
MR. LILLY: Okay. So --
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MS. MCCRACKEN: Related to the fish (indiscernible).
MR. LILLY: So just for the aquatic side, the main focus areas
were FA-104, Whiskers Slough. There are two aquatic transects, and
that one was located at the lower end of Whiskers Slough.
One was located in the Whiskers side channel at the upper end.
It was one of the identified chum spawning areas. There were wells
in surface water measurements and temperature profiles
(indiscernible) put in to both of those sections. So those were the
main two aquatic sections.
The next one was at FA-113, at Oxbow 1. And that was really
because of the simple nature of a hydrologic system, that was a
single -- there's two wells, it's not really a transect because we're
right at the end of Oxbow 1. That was the second aquatic area to
look at where there are a variety of measurements being made, both
continuous and manual measurements.
The next key area for the aquatic studies was at FA-128, or
Slough 8A, and there's two primary aquatic sections in that. One is
in the middle side Channel 8A and that's in the -- for the -- for those
who were on the agency meetings, we walked right by that section
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when we went up during the October -- I think it was the
October 2012 field effort. And so you walked right by it. That was
near the confluence of what we're calling Slough 8A proper.
And then the second major transect in Slough 8A focus area is
up on Slough 8A itself. And in all of these transects are shown -- the
newest maps are in the technical memos that I refer you to, because
you're going to see what was installed in 2013, plus the additional
sites installed in 2014 and the transects are identified. So those maps
are all available in those technical memos when you reach that point
of review.
Then the next major focus area where we're looking at transect
type studies for aquatic was in FA-138, the Gold Creek focus area,
and that was looking at Slough 11 and at Upper Side Channel 11.
And the same general approach of having wells on either side
of the side channels, obviously for right next to the river. There's not
an opposite?? side, but if we had a side channel or slough that we
could have wells in both sides, such as upper side Channel 11 in FA
138, there's two wells on one side, two wells on the other side, we
have stream bed temperature profile measurements and we have
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water stage and water temperature that are all being measured in
those.
We also measure -- wherever we measure water where we
have pressure tranfusions, (indiscernible) water stage, we also
measure water temperature.
MS. MCCRACKEN: Okay. Thank you. And these are all
co-located with the HSE?
MR. LILLY: Yes.
MR. HILGERT: Yes, although FA-113, it's -- sorry. This is
Phil here. They were all co-located with FA-113, Slough 6A didn't
have any salmon spawning, so we didn't have any (indiscernible) in
those areas.
MR. MUNTER: This is Jim Munter again. One quick
modeling thing I'll follow up on. In your methodology for modeling,
you didn't talk about what to do if your river stage is going up
because it's raining cats and dogs and you need to put recharge into
the surface of your model. And are you -- do you have plans to
address that process?
MR. LILLY: Yes. In the three main riparian focus areas, and
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in FA-138, Gold Creek, we have summer precipitation gauges. So
we're directly measuring summer precips, along with the -- we also
get a good indication when it's raining cats and dogs with a time
lapse camera that we have out, so we can account for the do we need
to have precip coming in at the top of the box.
MR. MUNTER: All right.
MR. PADULA: Any questions for Michael? Great. Thank
you for another good day. We ran over a little bit today, but I
appreciate everybody staying with us.
We're starting again at 8:30 in the morning. Those who are
interested in ice processes, fisheries, instream flow study, riparian
instream flow study, riparian vegetation study (indiscernible) end of
the day tomorrow, we will confirm the amendments that have been
made and get that information out to you.
MR. DYOK: Right. We're actually compiling a running list,
and eventually we'll go over that tomorrow.
MR. PADULA: Okay. Thanks, everybody. See you
tomorrow.
4:49:28
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(Off record.)
SESSION RECESSED
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