HomeMy WebLinkAboutSummaryEcological
Flows
Science
Advisory
Board
October
22
&
23,
2013
Meeting
Summary
Page
1
of
23
Ecological Flows Science Advisory Board (EFSAB)
Meeting Summary Oct, 22-23 2013
Stan Adams Training Facility, Jordan Lake, Chapel Hill, NC
FINAL Approved for Distribution
Attendance (for both days unless otherwise noted)
Members
Mark Cantrell, USFWS (10/22 only)
Bob Christian, ECU (present 10/22; online
10/23))
Tom Cuffney, US Geological Survey
Linda Diebolt, NC League of Municipalities
Chris Goudreau, NC Wildlife Resources
Commission
Jeff Hinshaw, North Carolina State University
Amy Pickle, EMC, Duke (9/24 only))
Sam Pearsall, Environmental Defense Fund
Judy Ratcliffe, NC Natural Heritage Program
(10/22 only)
Jaime Robinson, CH2MHill
Fred Tarver, NC Division of Water Resources
Division of Water Resources
Harold Brady
Alternates
Sarah McRae, US Fish & Wildlife (10/23)
Vann Stancil, NC Wildlife Resources
Commission
Tom Thompson, Duke Energy
David Williams, Div. SWC
Tom Gerow, NC Forest Service
Guests:
Jennifer Phelan (10/22 only)
NCSU Facilitation Team
Mary Lou Addor, NC State
University/NRLI
Christy Perrin, NC State University/WECO
Nancy Sharpless, NRLI
The purpose of the Ecological Flows Science Advisory Board: The Ecological Flows Science
Advisory Board (EFSAB) will advise NC Department Environment and Natural Resources (NCDENR)
on an approach to characterize the aquatic ecology of different river basins and methods to determine
the flows needed to maintain ecological integrity.
Presentations, reports, and background information of the EFSAB are available at:
http://ncwater.org/?page=366 (please note that this URL is new as of August 2013)
Much of the discussion among the EFSAB at the October 22 and 23, 2013
meetings is captured in the final report of the EFSAB rather than in this
meeting summary. The final report has been submitted to the Department of
Environment and Natural Resources.
Ecological
Flows
Science
Advisory
Board
October
22
&
23,
2013
Meeting
Summary
Page
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of
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October
22
&
23,
2013:
Summary
of
Decisions,
Recommendations
and
Proposed
Actions
Decisions and Recommendations:
1. The group reached consensus for including the RTI-USGS report as an Appendix for
reference in the EFSAB Report.
2. The EFSAB agreed that in discussion of the 2 strategies, under #1 (line 632 of version
4.1), the first sentence should be revised to say: The percentage of flow strategy
using 80-90% flow-by combined with a critical low flow component as the ecological
flow threshold.
3. The writing group assigned to revise the language for addressing a critical low flow
component of the statewide recommendation presented their revisions. The
revisions were approved and incorporated into the Final Report on page 20, under
Section 3.1.1 Percentage of Flow Strategy.
4. The EFSAB reached consensus on removing what had originally been #1 (then
became new #4) in the section on “Evaluating Potential for Ecological Impacts of
Future Water Use”, and then opted to remove the heading “Evaluating Potential for
Ecological Impacts of Future Water Use”. See Final Report for the final language of
this entire section on page 19, under Section 3.1.1 Percentage of Flow Strategy.
5. The group reached consensus on a revised Adaptive Management recommendation:
There is uncertainty in the science and the existing models, thus a risk-
averse strategy was used when devising recommendations. Changes in
climate and land use are expected to have significant effects on patterns of
temperature, precipitation, hydrology and ecology. Monitoring and
predicting these changes will be critical for success in maintaining
ecological integrity of North Carolina’s rivers and streams. An adaptive
management approach is required to continually advance the science and
reduce areas of uncertainty. Therefore, DENR should:
1. Emphasize new data (hydrologic and biological) collection and
evaluation in headwaters, in the coastal plain, and in large rivers,
recognizing that current biological models and assumptions may not
address these systems.
2. Adopt/design/develop strategies to:
a. Validate ecological thresholds (strategies should be informed by
new data or research);
b. Track the impact of flow changes when they occur;
c. Modify characterizations, target flows, and thresholds based on
new data, changing conditions (e.g., land cover, precipitation,
hydrology) and lessons learned; and
d. Georeference nodes to facilitate analysis.
6. The group finalized and reached consensus on the language for the section of the
report addressing threatened and endangered species to:
“The flow requirements of listed species are often not fully understood. In order to
conserve state and federally listed species, the EFSAB recommends that the flow
needs of these species should be considered by the DENR in addition to the
standard recommendations offered in this report. For planning purposes, portions of
basins (e.g., nodes) that include listed species should be treated by DENR as
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Advisory
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needing additional analysis in consultation with the WRC, NMFS and USFWS. When
a decision moves beyond planning, then applicable environmental review documents
will be sought from appropriate agencies. The EFSAB also encourages DENR and
other appropriate agencies to support further research on the flow requirements of
listed species.”
7. Chris, Fred, and Linda will revise the Flow-Habitat section and submit it for the
EFSAB’s review by 10/31/13.
8. With the understanding that there was additional work to be done on the glossary,
acronyms and reference sections, labeling all figures and tables correctly, putting the
report into consistent outline format, searching for terms to be corrected [historic
versus historical, for example], re-writing the flow-habitat relationships section, and
making the use of articles consistent, the EFSAB reached full consensus on moving
the document forward and submitting it to DENR. The EFSAB would receive the
finalized document for final review before submission.
Proposed Actions:
1. The RTI/USGS team will recalculate P-value for the non-scaled intercept (table 16,
17).
Table
of
Contents
October
22
&
23,
2013:
Summary
of
Decisions,
Recommendations
and
Proposed
Actions
...
2
Table
of
Contents
...............................................................................................................................................
3
I.
Executive
Summary
.................................................................................................................................
3
II.
Oct.2013
Meeting
Orientations
and
Sept.
2013
Meeting
Summary
Approval
...................
11
III.
Presentation:
Overview
of
the
RTI/USGS
Report
....................................................................
11
IV.
Discussion:
Continued
Review
and
Development
of
EFSAB
Recommendations
.........
14
V.
Report
Review
.........................................................................................................................................
19
VI.
Orientation
to
the
October
23
Meeting
.......................................................................................
20
VII.
Discussion:
Continued
Review
and
Development
of
EFSAB
Recommendations
..........
20
VIII.
Discussion/Review
of
Requested
Edits
to
the
EFSAB
DRAFT
Report
...............................
22
I. Executive
Summary
TITLE: Overview of the RTI- USGS Report
Presenter: Jennifer Phelan, RTI International
Major Discussion items/concerns/questions:
• If you are an expert witness trying to tear this apart, what are the chinks in the armor?
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• Biggest problem is the data are over such a large time period- DENR monitoring occurs only
every 5 years in a basin. Though getting the type of relationships we’re getting with such broad
data tells me we’re picking up a pretty good signal.
• Are there ways going forward to validate the approach, in a standardized or supplemental data
collection, to do a number of stratified sites on an annual basis, looking at some of the outliers?
• Kim Meitzen’s work found that the same site over time was very messy from one day to the
other. A better strategy would be to wait 5-10 years, and then repeat this process. Routine,
annual sampling at same site would probably not lend clarity.
• It should be in your report that this is not a predictive model. If you have flow changes, what is
likely to happen to the biology in the state? It’s not an estimate of what will happen on a specific
creek.
• If somebody were to suggest another option besides the selection of the 80th percentile, the
90th shows the same strength.
Decisions Made: The group tested consensus for including the RTI-USGS report as an Appendix for
reference in the EFSAB Report – the group was at full consensus with all 1’s.
Proposed Actions or Identified Decisions to be made:
• The RTI/USGS team will recalculate P-value for the non-scaled intercept (table 16, 17)
Continued Review and Development of EFSAB Recommendations
TITLE: Discussion: Critical Low Flow
Major Discussion Items/Concerns/Questions:
• Critical low flow is important for maintaining ecological integrity.
• We have not had adequate time to determine a specific number.
• Asking DENR to identify a critical low flow is important.
• It is not just the number; it is how you react.
• The important point is to avoid a scenario where the 80% flow-by goes below the critical low-
flow. The critical low flow becomes the flag.
• You will sometimes hit the critical low flow without withdrawals during drought.
• I think it is the duration that we are concerned about. With a withdrawal scenario, the duration
of the low flow will be extended; we want it closer to the natural duration.
• I would hope it would identify not necessarily where the threshold was reached, but would
stimulate DENR to evaluate whether they have plans to react to droughts. I’m trying to think of
how this would work so just reaching the threshold under normal conditions wouldn’t cause
them to always do additional work. We want to link it in their planning tool to a duration; we’re
not saying what the duration or threshold is.
• The language in bold does not suggest the Board is recommending Alberta; it just uses Alberta
as an example.
• The Alberta paper cites a lot of different approaches. Many use 7Q10, which we do not want to
recommend.
• Should we refer to the paper as a review of methods and a proposed method?
• I don’t think that discussion of the Alberta paper belongs in the recommendations section
• How can we refer them to an undefined low-flow threshold?
• We encourage DENR to look at it and figure it out.
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Decisions Made:
1. The EFSAB agreed that in discussion of the 2 strategies, under #1 (line 632 of version
4.1), the first sentence should be revised to say: The percentage of flow strategy using
80-90% flow-by combined with a critical low flow component as the ecological flow
threshold.
2. The writing group assigned to revise the language for addressing a critical low flow
component of the statewide recommendation presented their revisions. The revisions
were approved and incorporated into the Final Report on page 20, under Section 3.1.1
Percentage of Flow Strategy.
TITLE: Discussion: Evaluating Potential for Ecological Impacts of Future Water Use (Flag-
raising)
In addition to editorial changes, discussion included:
• The permitted flows (in #1 in version 4.2) are grandfathered, not ecological flows.
• We should move #1 down to be # 4 (with new language), as an exception to the others.
(all yes)
• I agree. That’s how we did coastal and headwaters.
• Doesn’t it get included in prevailing conditions?
• Yes, but it isn’t attributing it directly to that. It gets blurred.
• Fransen isn’t going to put 80% flow-by in those nodes. He still wants to know, when looking at
the entire basin, what is going on that now cause that node to fail, using a different set of
criteria.
• Rewrite the section on the permitted flows. (Chris, Tom T., Jeff)
• The remaining #’s (now 1, 2, and 3) are really the green, yellow and red flags.
• Did I miss discussion on the “trimmed hydrology?”
• We were trying to understand how Tom Fransen ran through that process in the model. He used
the term Index B hydrology set, which we thought was too confusing. I suggested that we use
the term “trimmed hydrology data set’. He had it as 10-90. I thought it was better to define it
one time.
• Are you uncomfortable with using the trimmed data set? You’d rather use the full data set?
• If you run the model with the whole data set and it says you have exceeded the threshold, then
you run it with the trimmed data set, when we chop off those extremes, does it still raise a flag?
If the answer is no, then those are dealing with those extreme low or high flows, and the drought
protocols should be able to handle those things. But if it raises the flag even with those extreme
ends cut off then you have something you really need to look at.
• So it is the yellow versus red flag.
• One is to go evaluate the source of this. Is it extreme high or low flow or is it a particular water
usage pattern for that node.
• Or maybe that's one of those headwater nodes where there wasn't a great gage, or it wasn't
calibrated that well, so it doesn't have that great a hydrology set in the first place so they have to
figure it out.
• My impression was that statutory requirements, in the last sentence of the red flag section are a
pretty low bar. I would say, "and also provide...” Don't assume that the drought plans, etc.
necessary provide sufficient response.
• It's possible that a slight alteration by a lot of people might bring the usage back within the
ecological threshold or the critical low flow. Once you identify a flag going up, what we hope to
achieve is that we can recognize some modification, hopefully minor, that can bring us back to
achieving that ecological integrity. We should be explicit that that is what we would like to see
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happen. Our objective is that they evaluate it and see solutions that would bring things back to
maintaining ecological integrity.
• It should already meet the statutory requirements.
• We are getting away from our scientific advice when we start talking about statutory
requirements. I think we should strike that part and put in the ecological outcome we would like
to see come from further review.
• It should say the objective of the review is maintaining ecological integrity.
• For the yellow flag, it is really about jiggering things around so that you maintain ecological
integrity.
• This flag is one that will go up fairly often. We are trying to give DENR some direction that is
something they can actually do. We wanted to suggest that they review to see if they can make
adjustments to maintain the ecological integrity--get ahead of the curve while in the yellow.
Start talking.
• That's the point of the yellow flag. They can look at the current situation, then look at the 2050
projections, then if in those 2050 projections the flag goes up, they look at what uses should not
be allowed in the future, or need to be adjusted. There is a future and a current component to
this action.
• We should go ahead and refer to these as flags--green, yellow and red.
• If we have red, yellow and green flags for responding to the first recommendation, then we need
to identify the flagness of option number 2 (ecodeficit tool). We might say that diminishment of
biological condition of more than 5-10% constitutes raising a red flag under option 2.
• How to incorporate critical low flow component in [new] #1 so it doesn’t always exceed the
threshold?
• There are 2 separate evaluations- critical low flow is to see if you’re exceeding the duration.
• No, the threshold is the higher of the 2 values
• The CLF piece is complex- it will take more effort to develop the language; the concept is what
is important to convey.
• Should we leave it and let DENR figure it out?
• We need to convey the CLF component; we don’t need to define how it is used.
• [new] #3 should include same action items as in [new] #2 as well as “additional review”
• What is “unaltered?” (Is it different from baseline)
• [new] #4—We don’t want “ecological” in the recommendation- permitted flow is not an
ecological flow.
• We’re saying it is a surrogate in the models, not that it is an ecological flow.
• Why wouldn’t you run the permitted conditions?
• What are permitted conditions being used for here?
• To run in the model instead of a % flow-by
• How is that different than running prevailing condition? Why not say “not all prevailing
conditions will meet these ecological thresholds” and recommend DWR evaluate prevailing
conditions against future use?
• A suggested refocus- don’t advise DENR on an immovable piece (permitted flow). That is
already happening- that section should be deleted.
• What if upstream conditions above the node make it hard to meet permitted flow?
• This came from Fransen. He won’t put flow-by in nodes with permitted flows. He will need to
work it into the model anyway. He was maybe thinking current projects were kind of an eco-
flow, and wanted to differentiate. It is okay to delete.
• #4 gets into something not in our framework- a different process.
• This section includes suggestions for how they operate it.
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• To delete, it would leave a hole in how they evaluate those areas that may be different than
flow-by.
• Don’t lose the information- it’s okay to delete. Consider how to let people know how to deal with
existing permitted flows. Could raise it as something to consider in the adaptive management
recommendation.
• Ok, delete (new) #4. It’s not our duty to tell DENR what to do with permitted conditions-
it’s outside our reach.
Decisions Made:
The EFSAB reached consensus on removing what had originally been #1 (then became new #4)
in this section and opted to remove the heading “Evaluating Potential for Ecological Impacts of
Future Water Use”. See Final Report for the final language of this entire section on page 19,
under Section 3.1.1 Percentage of Flow Strategy.
TITLE: Discussion: Adaptive Management Section
An EFSAB member proposed the following to be incorporated into the adaptive management
recommendation:
• There needs to be a strong and clear statement that:
o There is growing strong evidence that climate change is occurring.
o It is difficult to determine the changes that will occur in the Southeast.
o Changes in precipitation and temperature resulting in alterations to the hydrologic balance
will affect flows in ways not predictable from historic records used for OASIS.
o These alterations will affect predictions at the time scale for planning, jeopardizing the value
of the exercise.
o Adaptive management must include recognition of these changes in climate.
The EFSAB discussed this proposal and other potential changes to the adaptive management
recommendation.
Major Discussion items/concerns/questions:
• Adding climate change may doom the report, though I agree with the suggestions.
• Can we refer to changes in precipitation and temperature without mentioning climate change?
• In the current recommendation, add a sentence- changes in hydrology, precipitation,
evapotranspiration
• Land use change is an immediate threat that is also not addressed here.
• I’m uncomfortable not to address the drivers of hydrologic change. Is this a conservative
framework? There are future scenarios that make this NOT conservative
• We’re not reducing uncertainty, either.
• I was the one who recommended not to explicitly mention climate change because I was
worried it would cause officials to shelve this document since there is skepticism in the Dept.
about whether human activity causes climate change. The possibility of public officials’ views
preventing scientific professionals from expressing the truth has chastened me. I second the
proposal to reintroduce climate change into the adaptive management section. The truth does
not need to be subordinate here.
• We’re hedging a bit based on how we think politicians will receive it.
• We are acknowledging that there is limitation of the OASIS model, since it uses a historical
record rather than predictions.
• WaterFALL can simulate climate change modeling.
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• Climate change is not the only reason you’ll want to use adaptive management. Land use is
even more likely to have an impact.
• Climate change could produce large and unpredictable changes in temperature and
precipitation. The unpredictability is unlike land use change.
• It should reflect a list of why we would want an adaptive management approach, including
climate change impacts and others.
Decisions Made:
1. The group reached consensus on a revised recommendation:
There is uncertainty in the science and the existing models, thus a risk-averse strategy
was used when devising recommendations. Changes in climate and land use are
expected to have significant effects on patterns of temperature, precipitation, hydrology
and ecology. Monitoring and predicting these changes will be critical for success in
maintaining ecological integrity of North Carolina’s rivers and streams. An adaptive
management approach is required to continually advance the science and reduce areas
of uncertainty. Therefore, DENR should:
1. Emphasize new data (hydrologic and biological) collection and evaluation in
headwaters, in the coastal plain, and in large rivers, recognizing that current biological
models and assumptions may not address these systems.
2. Adopt/design/develop strategies to:
a. Validate ecological thresholds (strategies should be informed by new data or
research);
b. Track the impact of flow changes when they occur;
c. Modify characterizations, target flows, and thresholds based on new data,
changing conditions (e.g., land cover, precipitation, hydrology) and lessons
learned; and
d. Georeference nodes to facilitate analysis.
TITLE: Discussion: Threatened and Endangered Species
The Board reviewed a rewrite of the recommendation regarding Threatened and Endangered Species
(T&E), which had been revised prior to this meeting. Among other revisions, the rewrite removed
language about T&E being broadly addressed by the PHABSIM approach.
Major Discussion items/concerns/questions:
• The gist of it is that the species-specific flow requirements of listed species are not fully
understood, and they are listed species. We have a greater obligation there. I don't feel that we
did a really robust evaluation of flow-habitat relationships for these species. The PHABSIM
piece was related to an unaltered flow, 80% of an unaltered flow. Our recommendation is not
about an unaltered flow. Ours is 80% of prevailing conditions.
• PHABSIM aside, in the analysis that was done with the ecodeficit tool, data for T&E are
included in a general sense.
• Wherever there are aquatic riparian listed species, DENR is already required to develop site-
specific management plans.
• Is the point that the PHABSIM results broadly address T&E through the various guilds? Even
though they are not specifically addressed, the PHABSIM work gives some indication?
• The PHABSIM results are not directly translated into our statewide recommendation. It is not a
direct translation. To say that T&E are broadly addressed by PHABSIM is correct, but to say
that they are addressed by the statewide recommendation we are making is not an accurate
statement to me.
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• Does it help to say that T&E are not directly addressed by the statewide recommendations and
add a statement that they may be addressed by the PHABSIM evaluations?
• What if we say that flow-habitat relationships for listed species have not been specifically
addressed by the statewide recommendations and, therefore, species-specific flow
requirements should be addressed on a site-specific basis?
• That's like saying we haven't addressed some other grouping of organisms. They are in the
water. They are of the taxa that we assessed by the various means.
• We are just saying that they be considered. I would also change "maximum protection" to
"adequate protection" or "appropriate".
• How about just protection.
• Add NMFS and remove NHP, leaving WRC and USFWS.
Decisions Made:
The group finalized and reached consensus on the language for the section of the report addressing
threatened and endangered species to:
“The flow requirements of listed species are often not fully understood. In order to conserve
state and federally listed species, the EFSAB recommends that the flow needs of these species
should be considered by the DENR in addition to the standard recommendations offered in this
report. For planning purposes, portions of basins (e.g., nodes) that include listed species
should be treated by DENR as needing additional analysis in consultation with the WRC, NMFS
and USFWS. When a decision moves beyond planning, then applicable environmental review
documents will be sought from appropriate agencies. The EFSAB also encourages DENR and
other appropriate agencies to support further research on the flow requirements of listed
species.”
TITLE: Discussion: Flow-Habitat Relationships
Fred Tarver had rewritten the section of the report on Flow-Habitat Relationships. His revised version
had since been reworked by Linda Diebolt, Chris Goudreau, and Jim Mead. Fred provided an overview
of his revisions including:
• Removed discussion of IFIM to simplify.
• Encapsulated work done in piedmont by Jim Mead and in mountains by Fred.
• Moved some of the tables and graphs to put into an appendix or be removed from the report
altogether and just put on the website.
• Tried to encapsulate through text what some of the graphs showed.
• Restructured to make more readable for potential readers who have not been immersed in the
work of the EFSAB.
• Added a couple of charts that better summarized the results in an understandable way.
The facilitator suggested that the Board not try to wordsmith the document as a group, but that they
instead provide comments and suggestions for the writing team that would further refine the section.
Major Discussion items/concerns/questions:
• For the outsider not immersed in the EFSAB's work, it still needs work. It is not understandable.
Being new to the Board, I do not know what the charts are showing, and the text does not
adequately clarify. Perhaps explanatory captions would help.
• Perhaps you could put at the beginning or the end of each section a description of what the
section is telling you.
• Add to each section in bold a description of the purpose of that section and what this section is
conveying (annotation below the title).
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• It's going to be difficult to make that section lay-worthy.
• It would be helpful to have Index B explained in terms of habitat.
• The point is that the recipient of the report is DENR.
• I have a co-worker who spent 4 hours reading that section with me. If you would like an
outsider who read the original to look at it and see if the re-write makes sense, let me know.
Proposed Actions or Identified Decisions to be made:
Chris, Fred, and Linda will revise this section and submit it for the EFSAB’s review by 10/31/13.
TITLE: Discussion: Report Review and Finalization
On October 22, the facilitator noted that the RTI/USGS Report would be finalized (adding a graph and
correcting a few minor typos) and included as Appendix D. The facilitator reviewed the documents
created for assessing the many comments and suggested revisions from the Board’s review of version
4.1 of the report prior to this meeting. For several sections of the report she had shown the original text
in 4.1, then showed the proposed revisions. The EFSAB divided into two groups. Everyone in one
group took the first half of the document showing proposed revisions; the other group took the other
half. Then each individual reviewed their half of the revisions, providing comments on whether they
agree with the change, and if not, why. The facilitators collected the comments.
The report was then revised on October 23 to version 4.2 based on comments/revisions provided on
October 22 and over night. The facilitator led a review of version 4.2 of the report beginning with issues
that the facilitators had identified as needing addressing.
Major Discussion items/concerns/questions:
• Acknowledgements (people who contributed to the process from the beginning)
• Update References
• What writing style to use?
• Executive Summary [Tom Cuffney will write one of approximately 2 pages]
• Removed section on tools [consensus]
• Title [Tom Cuffney will write]
• Photos to include
• Submitted to whom? [DENR]
• Add date.
• Tribute to Steve Reed
• Re-title some sections
• Number sections and subsections.
• Table of Contents
The Board then went through sections of the report, word-smithing some language. All of the changes
made are included in the final report.
Decision Made:
With the understanding that there was additional work to be done on the glossary, acronyms
and reference sections, labeling all figures and tables correctly, putting the report into
consistent outline format, searching for terms to be corrected [historic versus historical, for
example], re-writing the flow-habitat relationships section, and making the use of articles
consistent, the EFSAB reached full consensus on moving the document forward and submitting
it to DENR. The EFSAB would receive the finalized document for final review before
submission.
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II. Oct.
2013
Meeting
Orientations
and
Sept.
2013
Meeting
Summary
Approval
Members and alternates of the Ecological Board Science Advisory Board introduced themselves and
their affiliations. Guests in attendance and the facilitation team also introduced themselves. Everyone
who attended the meeting was reminded to sign-in.
A brief orientation was conducted of the meeting facilities (restrooms, concession) and available
technology (webinar).
The EFSAB approved the September 24 & 25, 2013 meeting summary, and it has been posted to the
NC Water.org website.
III. Presentation:
Overview
of
the
RTI/USGS
Report
Presenter: Jennifer Phelan, RTI
Jennifer provided an overview of the RTI-USGS report, chapter by chapter.
1. Purpose of report- to document NC data, methods and results of their work in support of ecological
flows.
2. Stream classification- with the proposed classification, we didn’t know the degree by which the
classes described the biology, which was the purpose of a bio fidelity analysis. We found that with the
classes developed using USGS data, the classes were very sensitive to flow metrics. As small as a
10% change in the period of record would cause a jump in stream class. When we tried to use
modeled data, we found only 50% match rate between USGS data and modeled data- we found it
indicated a problem with the classification. See Table 4 in the report.
This gave rise to the BEC, biological-environmental classification system. The objective was to develop
and implement an easy to understand system to apply all across the state. It wasn’t as easy as we
thought- we didn’t find any distinct stream classes that could be built. Pre-existing a-priori classes were
best: for benthics- Omernick Level 3; for fish-Ecological drainage units (EDU).
We didn’t gain anything further to add other physiographic variables.
3. Flow-biology relationships
She drew a graph of flow and biological response. A lot of effort went into this; we tried a lot of
approaches from hierarchal, statistical, biological perspectives. P. 16 is biological responses (and in
pp. 5-8). For fish- 156 species were measured in NC, grouped into 6 flow based habitat guilds. We did
analyses on sensitivity of guilds, found riffle run guild was most sensitive to alteration, and it had the
greatest distribution across the state. We adopted that as response metric for fish. We could
characterize fish by abundance, species richness, or Shannon-Weaver Diversity index, which
integrated the 2 so we chose that one.
Tom Cuffney spent time on methods for benthos. We looked at 108 metrics, evaluated them on how
well they responded, range over which they responded, and relevance to state for assessing water
quality. We chose EPT Richness.
For flow change, we recommended using WaterFALL model because we could generate records at
each biological monitoring station. We used PNV (potential natural vegetation) layer vs. 2006 NLCD as
current land use, which is the full human influence of flow alteration plus land use. We used a 1967-
2006 climate record.
That’s the hydrology data. For flow metrics, 94 were evaluated (pp. 18-19); some came from TNC, and
some from Vogel et al. We developed a list based on goals of NC, in consultation with Fred and Jim,
and focused on those that were meaningful to management in the state, and focused on reductions in
flow. Then we went through an iterative process to narrow them down. A large number of metrics were
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highly correlated (like month by month). The final list of metrics is on p. 21, Table 9. Six metrics were
selected because they were useful for management; focused on reductions of low flows, represent
magnitude, timing, and duration of flow. They could also be modeled by WaterFALL and have a low
degree of intercorrelation redundancy.
This resulted in a total of 12 potential relationships (with flow metrics on x axis –, biological response on
y axis). The following steps were then taken.
Step 1: Determine what type of regression we wanted to attempt. You can see the data looks a little
messy. Based on literature regarding ecology and flow biology relationships, we tried to focus on upper
limits of response, using quantile regression. This represents the upper limit of biological response
attributed to the x-axis. Everything below is also influenced by something else. We chose 2 possible
analytical approaches that focused on that: 80th quantile regression, and also the upper limit
regression, which took the upper 20% data and drew line. 80th quantile is most scientifically defensible
as it was used in Potomac and other literature. Figures 9-10 show these processes.
Step 2: Determine if we should describe relationships as linear or non-linear. We saw a drop in
response. Regarding the significance of relationships, in some cases it was linear or non linear. For
management purposes, we decided to adopt the linear relationship since it’s easier for managers to
adopt.
Step 3: Decide whether to do the flow-biology relationships by region or state. The BEC class system
was by a priori class systems- Omernick level 3, ecological drainage units for fish. We were not very
successful developing flow-biological relationships by class. That might be due to not enough data.
But we had strong significant relationships statewide.
Step 4: Decide whether to normalize data or use raw data for state level analyses. If analyzed at state
level, we should account for inter-basin variation. Table 12-13 shows why we should do normalization.
There were variations between basins. Much appreciation to Tom for pointing this out- maybe some of
the variation is due to variation of hydrology in the basins. It turned out to be the case. Figures 14-15
shows EPT richness by eco-region, divided by excellent (reference) sites. In general the reference
sites in mountains have higher EPT richness than piedmont, than coastal. Figure 15 focuses on
excellent sites, where you see the inverse is true. The mountains have the lowest amounts of flow
alteration; the piedmont has more altered hydrology. We did back-casting and found a larger portion of
changes in biology could be attributed to altered hydrology. This showed we did not need to normalize;
we could use the raw data.
We did a statewide analysis, linear regression, on raw data.
Q: The fact you did it on raw data makes sense. Are there any other sources in literature to justify that
decision? You’re using raw data for EPT. I would expect it to change between mountain and
piedmont, coastal, regardless of hydrology. Some of the change would be due to normal differences;
some would be attributed to man-made hydrology
R: These are sites that are naturally different in hydrology. These are excellent sites. You’re not
looking at flow alteration per se. If we had normalized it we would compound the errors.
R: State level analysis- I’m not aware if anyone has done anything on this large of a scale. You do
have portion of table showing what deviation is accountable by flow.
Q: Use of excellent, good classes in coastal plain. I don’t know if this is an EPT thing or fish. They use
the term natural condition in the coastal plain; they pulled away from using the excellent, good, good-
fair for swamp systems. Curious how that was addressed in coastal plain.
R: For invertebrates the state is still using good, excellent, fair.
Q: Fishes have a natural swamp condition not included in the classification system.
R: We didn’t adopt the state’s fish classification system. We produced an index comparable to benthic
class. For each basin took 80th percentile, then took 80th percentile of that- the best of the best for what
that could be for fish.
Q: What do you think the chinks in the armor are on this? If you were an expert witness trying to tear it
apart, what would you say?
R: Biggest problem is the data are over such a large time period. Every 5 years they go back to
monitor in a basin. 1989 was earliest record. We took the most recent record for each site. Getting
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the type of relationships we’re getting with such broad data tells me we’re picking up a pretty good
signal.
Q: If you had more info, do you think the regional models would have shown more significance? It’s a
subjective question. The regional models didn’t show as much significance but you’d hope to see it if
you had the data to back it up.
R: A lot of the break down has been in trying to compartmentalize, because these things are
continuous. If you have discrete units and you’re sampling away from the edges you may get good
differentiation, but in reality these things don’t have hard edges. Also the number of sites is huge.
Q: Are there ways going forward to validate the approach, in a standardized or supplemental data
collection, to do a number of stratified sites on an annual basis, looking at some of the outliers?
R: Think about Kim Meitzen’s work- she found that the same site over time was very messy. She
found so much influencing biology one day to the other.
R: A better strategy would be to wait 5-10 years, and then repeat this process. Take parts that worked
well, now looking at another 2 data points for each site and see if you come up with similar set of
relationships. I would consider that strongly validated. Routine, annual sampling at same site would
probably not lend clarity.
Important, this tells us this is the reaction over the state on average. It is not predicting what is
happening at a single site. If you want to undermine it in a statistical way, go to a single site and try to
predict what will happen. It’s just there to tell you that you have a probability of having an account.
Think of what’s going into this. You have a 40-year record, also not acknowledging the Clean Water
Act and changes that may have happened in water quality. Keep in mind what has gone into the
relationships and the strength.
Q: Was that comment included in SAB report? Statement that it is not a site-specific model where you
could take and predict a response at a site?
R: It should be in your report- its’ not a predictive model. You want to know what potentially can
happen. You don’t want many models at each site. What you want to know, if you have flow changes,
what is likely to happen to the biology in the state. It’s not an estimate of what will happen on a specific
creek.
Q: Do you think you’d have same level of success if you used other guilds?
R: Yes, for invertebrates there are others that would work. Average tolerance worked well but didn’t
have the same range as species richness.
C: On the fish side, a balance of number of data points and sensitivity. We did look at pools, showed
less sensitive. Riffle guild was most sensitive.
R: It’s not documented here, but we will put into a manuscript the contrast between riffle-run and pool
guild. In many ways that would be good to include, it supports the whole theory. Yes our sensitive
guilds are responding more strongly than less sensitive guilds (pool).
C: It’s not necessary for us to include in our report.
C: Anyone who questions it could go to that document, which would be peer reviewed.
Q: The selection of the 80th percentile, is that another item that someone might suggest other options
that could have been chosen?
R: If somebody was upset by it we could do the 90th percentile. 90th shows the same strength
Are there any other holes, things we need to defend?
With respect to final product, refer to figures on pp. 34, 35…these are what we’d recommend to include
in your report, on these pages.
Q: Specific to this graph, don’t you force your intercept to be 100?
R: When you scale.
Q: P value was for what?
R: For the true intercept, we may have to re-do that to put the non-scaled intercept (table 16, 17)
C: You may want to check that.
Chapter 4- ecological flow framework- the idea behind it was to place flow-biology curves into a
management framework, as there was no obvious threshold that could be adopted. That gave us the
driver to develop an ecological flow framework, which was the working river concept that is behind
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Table 18. For rivers with excellent conditions of flow, allow only 5% change in biology. If good, less
allowed. It shows how the flow framework fits onto those curves. Finally, we showed 2 contrasting
stream segments that are different by size and alteration of flows.
The other thing we wanted to highlight with this approach using the Neuse and Eno was to show how
the % ecodeficit looks different based on difference in size of river. Tables 20-23, shows how you need
to do it on a season-by-season basis. Summer ecodeficit is different than winter ecodeficit.
That’s it. Any other questions, thoughts, or concerns?
None.
Decision: The group tested consensus for including the RTI-USGS report as an Appendix for
reference in the EFSAB Report – the group was at full consensus with all 1’s.
IV. Discussion:
Continued
Review
and
Development
of
EFSAB
Recommendations
Comments made by EFSAB members on the draft report prior to this meeting had indicated areas of
the recommendations that needed to be revisited for clarification and agreement. The facilitators
provided a list of those areas that they identified:
1. Critical Low Flow
2. Statewide Ecological Flow Evaluation
3. Ensure that the scenarios for when a flag is raised are described completely.
4. Adaptive Management Recommendation—consider adding climate change
5. What else?
Critical Low Flow
The Board began by reading the revised recommendations section (version 4.1). They then discussed
the section on critical low flow. In addition to some editorial comments, substantive comments
included:
• Critical low flow is important for maintaining ecological integrity.
• We have not had adequate time to determine a specific number.
• Asking DENR to identify a critical low flow is important.
• It is not just the number; it is how you react.
• The important point is to avoid a scenario where the 80% flow-by goes below the critical low-
flow. The critical low flow becomes the flag.
• You will sometimes hit the critical low flow without withdrawals during drought.
• I think it is the duration that we are concerned about. With a withdrawal scenario, the duration
of the low flow will be extended; we want it closer to the natural duration.
• I would hope it would identify not necessarily where the threshold was reached, but would
stimulate DENR to evaluate whether they have plans to react to droughts. I’m trying to think of
how this would work so just reaching the threshold under normal conditions wouldn’t cause
them to always do additional work. We want to link it in their planning tool to a duration; we’re
not saying what the duration or threshold is.
• When we rewrote that section, we got away from specific % flow-by and critical low flow
numbers. Whatever DENR figures out its part of this evaluation. We have a pretty good
handle on the % flow-by since Fransen provided that example. But we haven’t discussed the
critical low flow, if not the number then the duration. If there has to be additional language that
addresses that, maybe that gets everyone on the same page.
• Is anyone uncomfortable with the Alberta Method?
• Yes, they basically shoot down their own method a lot in there. They use weekly rather than
daily time steps…its pretty much focused on a couple basins. It shouldn’t prevent us with
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including a critical low flow just because it doesn’t apply well to NC. We haven’t had the
opportunity to see what it looks like for NC streams.
• The language in bold does not suggest the Board is recommending Alberta; it just uses Alberta
as an example.
• The Alberta paper cites a lot of different approaches. Many use 7Q10, which we do not want to
recommend.
• Should we refer to the paper as a review of methods and a proposed method?
• I don’t think that discussion of the Alberta paper belongs in the recommendations section
• How can we refer them to an undefined low-flow threshold?
• We encourage DENR to look at it and figure it out.
The EFSAB agreed that Jaime, Chris, Fred and Jeff would revise the discussion of critical low-
flow in the report and present that to the EFSAB after lunch.
The EFSAB also agreed (all 1’s) that in discussion of the 2 tools, under #1 (line 632 of version
4.1), the first sentence should be revised to say: In the basin wide hydrologic models, use 80-
90% flow-by combined with a critical low flow component as the ecological flow threshold.
Discussion About Evaluating Potential for Ecological Impacts of Future
Water Use
(Flag-raising)
In addition to editorial changes, discussion included:
• The permitted flows (in #1 in version 4.2) are grandfathered, not ecological flows.
• We should move #1 down to be # 4 (with new language), as an exception to the others.
(All yes)
• I agree. That’s how we did coastal and headwaters.
• Remove “In the absence of permitted flow requirements” from line 751, then #2 becomes #1.
• Don't use the word “deemed”
• Doesn’t it get included in prevailing conditions?
• Yes, but it isn’t attributing it directly to that. It gets blurred.
• Fransen isn’t going to put 80% flow-by in those nodes. He still wants to know, when looking at
the entire basin, what is going on does that now cause that node to now fail, using a different
set of criteria.
• Rewrite the section on the permitted flows. (Chris, Tom T., Jeff)
• The remaining #’s (now 1, 2, and 3) are really the green, yellow and red flags.
• Did I miss discussion on the “trimmed hydrology?”
• We were trying to understand how Tom Fransen ran through that process in the model. He used
the term Index B hydrology set, which we thought was too confusing. I suggested that we use
the term “trimmed hydrology data set”. He had it as 10-90. I thought it was better to define it
one time. If somebody has a better way of saying it, that’s great.
• I have seen that term.
• We need to be careful about the extent to which DENR influences our advice to them. It seems
like they are writing a handbook along with our advice. Let’s make sure what we write
constitutes our best scientific advice and let DENR do what they can with it.
• This came about because last time we agreed that we would use Fransen’s basic flag-raising
approach.
• Are you uncomfortable with using the trimmed data set? You’d rather use the full data set?
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• If you run the model with the whole data set and it says you have exceeded the threshold, then
you run it with the trimmed data set, when we chop off those extremes, does it still raise a flag?
If the answer is no, then those are dealing with those extreme low or high flows, and the drought
protocols should be able to handle those things. But if it raises the flag even with those extreme
ends cut off then you have something you really need to look at.
• So it is the yellow versus red flag.
• One is to go evaluate the source of this. Is it extreme high or low flow or is it a particular water
usage pattern for that node.
• Or maybe that's one of those headwater nodes where there wasn't a great gage, or it wasn't
calibrated that well, so it doesn't have that great a hydrology set in the first place so they have to
figure it out.
• My impression was that statutory requirements, in the last sentence of the red flag section, is a
pretty low bar. I would say, "and also provide...” Don't assume that the drought plans, etc.
necessary provide sufficient response.
• It's possible that a slight alteration by a lot of people might bring the usage back within the
ecological threshold or the critical low flow. Once you identify a flag going up, what we hope to
achieve is that we can recognize some modification, hopefully minor, that can bring us back to
achieving that ecological integrity. We should be explicit that that is what we would like to see
happen. Our objective is that they evaluate it and see solutions that would bring things back to
maintaining ecological integrity.
• Be above the threshold.
• It should already meet the statutory requirements.
• We are getting away from our scientific advice when we start talking about statutory
requirements. I think we should strike that part and put in the ecological outcome we would like
to see come from further review.
• It should say the objective of the review is maintaining ecological integrity.
• For the yellow flag, it is really about jiggering things around so that you maintain ecological
integrity.
• It is demand-side management, basically.
• This flag is one that will go up fairly often. We are trying to give DENR some direction that is
something they can actually do. We wanted to suggest that they review to see if they can make
adjustments to maintain the ecological integrity--get ahead of the curve while in the yellow.
Start talking.
• That's the point of the yellow flag. They can look at the current situation, then look at the 2050
projections, then if in those 2050 projections the flag goes up, they look at what uses should not
be allowed in the future, or need to be adjusted. There is a future and a current component to
this action.
• We should go ahead and refer to these as flags--green, yellow and red.
• In line 735, we have a subtitle. We should not have a subtitle there. Also, if we have red,
yellow and green flags for responding to the first recommendation, then we need to identify the
flagness of option number 2 (ecodeficit tool). We might say that diminishment of biological
condition of more than 5-10% constitutes raising a red flag under option 2.
• The EFSAB decided that a small group would work on rewriting this section and present
to the group.
During lunch, a small group made revisions to a section of the Statewide Ecological Flow Evaluation
recommendation called: Evaluating Potential for Ecological Impacts of Future Water Use
The language in 4.2 for this section included a bullet starting “Existing permitted flow requirements
(e.g., FERC licenses) will be deemed as ecological threshold levels”. The following discussion referred
to this section as well as how to evaluate critical low flows.
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• How to incorporate critical low flow component in #1 so it doesn’t always exceed the threshold?
• There are 2 separate evaluations- critical low flow is to see if you’re exceeding the duration.
• No, the threshold is the higher of the 2 values
• The CLF piece is complex- it will take more effort to develop the language; the concept is what
is important to convey.
• Should we leave it and let DENR figure it out?
• This is a repeat of the ecological flow recommendation. It is incomplete because our analysis is
incomplete. We need to convey the CLF component; we don’t need to define how it is used.
• #3 should include same action items as in #2 as well as “additional review”
• What is “unaltered?” (Is it different from baseline)
• #4 don’t want “ecological” in the recommendation- permitted flow is not an ecological flow.
• We’re saying it is a surrogate in the models, not that it is an ecological flow.
• Why wouldn’t you run the permitted conditions?
• What are permitted conditions being used for here?
• To run in the model instead of a % flow-by
• How is that different than running prevailing condition? Why not say “not all prevailing
conditions will meet these ecological thresholds” and recommend DWR evaluate prevailing
conditions against future use?
• A suggested refocus- don’t advise DENR on an immovable piece (permitted flow). That is
already happening- that section should be deleted.
• What if upstream conditions above the node make it hard to meet permitted flow?
• This came from Fransen. He won’t put flow-by in nodes with permitted flows. He will need to
work it into the model anyway. He was maybe thinking current projects were kind of an eco-
flow, and wanted to differentiate. It is okay to delete.
• #4 gets into something not in our framework- a different process.
• This section includes suggestions for how they operate it.
• To delete, it would leave a hole in how they evaluate those areas that may be different than
flow-by.
• Don’t lose the information- it’s okay to delete. Consider how to let people know how to deal with
existing permitted flows. Could raise it as something to consider in the adaptive management
recommendation.
• Ok, delete (new) #4. It’s not our duty to tell DENR what to do with permitted conditions-
it’s outside our reach.
The EFSAB reached consensus on removing (new) #4 in this section and opted to remove the
heading “Evaluating Potential for Ecological Impacts of Future Water Use”. See Final Report for
the final language of this entire section on page 19, under Section 3.1.1 Percentage of Flow
Strategy.
Discussion about Adaptive Management Recommendation
An EFSAB member proposed the following to be incorporated into the adaptive management
recommendation:
• There needs to be a strong and clear statement that:
o There is growing strong evidence that climate change is occurring.
o It is difficult to determine the changes that will occur in the Southeast.
o Changes in precipitation and temperature resulting in alterations to the hydrologic balance
will affect flows in ways not predictable from historic records used for OASIS.
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o These alterations will affect predictions at the time scale for planning, jeopardizing the value
of the exercise.
o Adaptive management must include recognition of these changes in climate.
The EFSAB discussed this proposal and other potential changes to the adaptive management
recommendation. The main points of their discussion follow here:
• Adding climate change may doom the report, though I agree with the suggestions.
• Can we refer to changes in precipitation and temperature without mentioning climate change?
• In the current recommendation, add a sentence- changes in hydrology, precipitation,
evapotranspiration
• Land use change is an immediate threat that is also not addressed here.
• #3c “changing conditions” covers all that
• Add (e.g. land cover, hydrology, precipitation)
• Add “emphasize new data collection in headwater streams”
• Add something about permitted flows here? (no)
• Do we address the high end of the hydrograph? (That is in the front part of the document)
• Specify types of data? (biological, hydrological)
Changes were made to reflect this discussion.
Facilitator: does this section meet your interests?
• I think we should better address climate change but I don’t want to hold this up.
• I’m uncomfortable not to address the drivers of hydrologic change. Is this a conservative
framework? There are future scenarios that make this NOT conservative
• We’re not reducing uncertainty, either.
• Could we couch climate change in phrases that we haven’t explored? We would acknowledge
that we expect to have impacts but haven’t explored them, as an introductory paragraph of the
adaptive management recommendation.
• Add- monitoring and predicting changes in temperature and precipitation.
The EFSAB made edits to the adaptive management recommendation that incorporated the
concerns discussed. [Facilitators’ note: Further changes were made the following morning.]
Revisit Threatened and Endangered Species Recommendation
The Board took a few minutes to review the rewrite of the recommendation regarding Threatened and
Endangered Species (T&E), which had been revised prior to this meeting. Among other revisions, the
rewrite removed language about T&E being broadly addressed by the PHABSIM approach. Comments
and discussion points included:
• The gist of it is that the species-specific flow requirements of listed species are not fully
understood, and they are listed species. We have a greater obligation there. I don't feel that we
did a really robust evaluation of flow-habitat relationships for these species. The PHABSIM
piece was related to an unaltered flow, 80% of an unaltered flow. Our recommendation is not
about an unaltered flow. Ours is 80% of prevailing conditions.
• PHABSIM aside, in the analysis that was done with the ecodeficit tool data for T&E are included
in a general sense.
• Not sturgeons; not freshwater mussels.
• To say that we have not addressed T&E at all I think is not...
• I'm not saying that we did not address them at all. I'm saying...
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• If it is flowing from the rest of the document, then this paragraph is dealing specifically with T&E.
Wherever there are aquatic riparian listed species, DENR is already required to develop site-
specific management plans.
• Is the point that the PHABSIM results broadly address T&E through the various guilds? Even
though they are not specifically addressed, the PHABSIM work gives some indication?
• For some species we developed some really specific...
• Absolutely.
• The PHABSIM results are not directly translated into our statewide recommendation. It is not a
direct translation. To say that T&E are broadly addressed by PHABSIM is correct, but to say
that they are addressed by the statewide recommendation we are making is not an accurate
statement to me.
• Does it help to say that T&E are not directly addressed by the statewide recommendations and
add a statement that they may be addressed by the PHABSIM evaluations?
• Again, I don't think we need to put a caveat in there that would be an out where you wouldn't
consider listed species separately.
• What if we say that? What if we say that flow-habitat relationships for listed species have not
been specifically addressed by the statewide recommendations and therefore species-specific
flow requirements should be addressed on a site-specific basis?
• That's like saying we haven't addressed some other grouping of organisms. They are in the
water. They are of the taxa that we assessed by the various means. I don't see it as a big deal.
• If you lead off with the second sentence, saying that they are not fully understood, strike
potentially more limiting because we are not trying to lead people. We are just saying that they
be considered. I would also change "maximum protection" to "adequate protection" or
"appropriate".
• How about just protection.
• I like the first sentence; I think it is a good introduction to the paragraph.
• Add NMFS and remove NHP, leaving WRC and USFWS.
The Board opted revisit the proposed changes the next day.
V. Report
Review
The facilitator noted that the Board will have completed the substance of their recommendations once
the Board approves the T&E. The next step would be to finalize the report. The facilitator noted that
the RTI/USGS will be finalized (adding a graph and correcting a few minor typos) and included as
Appendix D. The revisions to the Flow-Habitat Relationships section of the report were also not
included in the version of the report that the Board was working with today. Chris, Linda, and Fred had
been working on revising that section to improve readability for anyone not immersed in the work of the
EFSAB. Those revisions would be sent out this night and reviewed on the second day of this meeting.
The facilitator reviewed the documents created for assessing the many comments and suggested
revisions from the Board’s review of version 4.1 of the report prior to this meeting. For several sections
of the report she had shown the original text in 4.1, then shown the proposed revisions. The EFSAB
divided into two groups. Everyone in one group took the first half of the document showing proposed
revisions; the other group took the other half. Then each individual reviewed their half of the revisions,
providing comments on whether they agree with the change, and if not, why. The facilitators collected
the comments.
The meeting adjourned.
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VI. Orientation
to
the
October
23
Meeting
After introductions, the facilitators introduced the agenda for the day:
• Revisit the flow-habitat relationships section
• Revisit Critical Low Flow
• Revisit the Adaptive Management Section
• Revisit the Threatened and Endangered Section
• Review and revise sections of the report, which had received conflicting comments/proposed
revisions
VII.
Discussion:
Continued
Review
and
Development
of
EFSAB
Recommendations
Threatened and Endangered Species
The group finalized and reached consensus on the language for the section of the report addressing
threatened and endangered species to:
“The flow requirements of listed species are often not fully understood. In order to conserve
state and federally listed species, the EFSAB recommends that the flow needs of these species
should be considered by the DENR in addition to the standard recommendations offered in this
report. For planning purposes, portions of basins (e.g., nodes) that include listed species
should be treated by DENR as needing additional analysis in consultation with the WRC, NMFS
and USFWS. When a decision moves beyond planning, then applicable environmental review
documents will be sought from appropriate agencies. The EFSAB also encourages DENR and
other appropriate agencies to support further research on the flow requirements of listed
species.”
Revisit the Adaptive Management Section
An EFSAB member asked to revisit the Adaptive management recommendation, to better address his
interest in communicating the importance of addressing hydrologic changes due to climate change.
Suggestions to amend the recommendation were sent.
Discussion points:
• I was the one who recommended not to explicitly mentioning climate change because I was
worried it would cause officials to shelve this document since there is skepticism in the Dept.
about whether human activity causes climate change. The possibility of public officials’ views
preventing scientific professionals from expressing the truth has chastened me. I second the
proposal to reintroduce climate change into the adaptive management section. The truth does
not need to be subordinate here.
• We include consideration of the effects; we haven’t included the term.
Ecological
Flows
Science
Advisory
Board
October
22
&
23,
2013
Meeting
Summary
Page
21
of
23
• What they would react to is whether it is anthropogenic, so include whether it is anthropogenic
or naturally caused- the fact that it is happening is what is important, not the causes.
• Why emphasize those differences?
• Including “natural” may help make it more likely to be read.
• We’re hedging a bit based on how we think it will be received by politicians.
• We are acknowledging that there is limitation of the OASIS model, since it uses a historical
record rather than predictions.
• WaterFALL can simulate climate change modeling.
• Climate change is not the only reason you’ll want to use adaptive management. Land use is
even more likely to have an impact.
• Climate change could produce large and unpredictable changes in temperature and
precipitation. The unpredictability is unlike land use change.
• It should reflect a list of why we would want an adaptive management approach, including
climate change impacts and others.
The group worked together and revised the recommendation to meet their interests.
Resulting recommendation:
There is uncertainty in the science and the existing models, thus a risk-averse strategy was
used when devising recommendations. Changes in climate and land use are expected to have
significant effects on patterns of temperature, precipitation, hydrology and ecology. Monitoring
and predicting these changes will be critical for success in maintaining ecological integrity of
North Carolina’s rivers and streams. An adaptive management approach is required to
continually advance the science and reduce areas of uncertainty. Therefore, DENR should:
1. Emphasize new data (hydrologic and biological) collection and evaluation in headwaters, in
the coastal plain, and in large rivers, recognizing that current biological models and
assumptions may not address these systems.
2. Adopt/design/develop strategies to:
a. Validate ecological thresholds (strategies should be informed by new data or
research);
b. Track the impact of flow changes when they occur;
c. Modify characterizations, target flows, and thresholds based on new data, changing
conditions (e.g., land cover, precipitation, hydrology) and lessons learned; and
d. Georeference nodes to facilitate analysis.
Decision: Consensus was tested- all EFSAB members accepted the recommendation (all
one’s.)
Revisit Critical Low Flow
The writing group assigned to revise the language for addressing a critical low flow component of the
statewide recommendation presented their revisions. The revisions were approved and
incorporated into the Final Report on page 20, under Section 3.1.1 Percentage of Flow Strategy.
Revisit Flow-Habitat Relationships
Fred Tarver had rewritten the section of the report on Flow-Habitat Relationships. Linda Diebolt, Chris
Goudreau, and Jim Mead had since reworked his revised version. Fred provided an overview of his
revisions including:
• Removed discussion of IFIM to simplify.
• Encapsulated work done in piedmont by Jim Mead and in mountains by Fred.
Ecological
Flows
Science
Advisory
Board
October
22
&
23,
2013
Meeting
Summary
Page
22
of
23
• Moved some of the tables and graphs to put into an appendix or be removed from the report
altogether and just put on the website.
• Tried to encapsulate through text what some of the graphs showed.
• Restructured to make more readable for potential readers who have not been immersed in the
work of the EFSAB.
• Added a couple of charts that better summarized the results in an understandable way.
The facilitator suggested that the Board not try to wordsmith the document as a group, but that they
instead provide comments and suggestions for the writing team that would further refine the section.
EFSAB comments included:
• For the outsider not immersed in the EFSAB's work, it still needs work. It is not understandable.
Being new to the Board, I do not know what the charts are showing, and the text does not
adequately clarify. Perhaps explanatory captions would help.
• The figure captions could be more explanatory.
• Perhaps you could put at the beginning or the end of each section a description of what the
section is telling you.
• Add to each section in bold a description of the purpose of that section and what this section is
conveying (annotation below the title).
• It's still dense.
• That's okay if it has to be, but then it needs to be explained.
• It's going to be difficult to make that section lay-worthy.
• It would be helpful to have Index B explained in terms of habitat.
• The point is that the recipient of the report is DENR.
• I don't think all sections of the report need a Reader's Digest summary.
• I have a co-worker who spent 4 hours reading that section with me. If you would like an
outsider who read the original to look at it and see if the re-write makes sense, let me know. I
have permission from the company for her to do that on the clock, and she is available to do it.
Chris, Fred, and Linda will revise this section and submit it by 10/31/13.
What Else?
The facilitator then asked if the EFSAB identified any remaining areas that need addressing in the
recommendations.
• A section that was redundant was removed.
• Board members suggested changing some language in places. These changes are captured in
the final report.
VIII. Discussion/Review
of
Requested
Edits
to
the
EFSAB
DRAFT
Report
The facilitator led a review of the report beginning with issues that the facilitators had identified as
needing addressing. Discussions included:
Acknowledgements (people who contributed to the process from the beginning)
Update References
What writing style to use?
Executive Summary [Tom Cuffney will write one of approximately 2 pages]
Ecological
Flows
Science
Advisory
Board
October
22
&
23,
2013
Meeting
Summary
Page
23
of
23
Removed section on tools [consensus]
Title [Tom Cuffney will write]
Photos to include
Submitted to whom? [DENR]
Add date.
Tribute to Steve Reed
Re-title some sections
Number sections and subsections.
Table of Contents
The Board then went through sections of the report, word-smithing some language. All of the changes
made are included in the final report.
With the understanding that there was additional work to be done on the glossary, acronyms
and reference sections, labeling all figures and tables correctly, putting the report into
consistent outline format, searching for terms to be corrected [historic versus historical, for
example], re-writing the flow-habitat relationships section, and use of articles, the EFSAB
reached full consensus [all ones] on moving the document forward and submitting it to DENR.
The EFSAB would receive the finalized document for final review before submission.
The facilitator congratulated the EFSAB on completion of their work.