WEBVTT
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Language: en

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What is Ecological Drought?

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Exploring its impacts on natural and cultural
resources

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John Ossanna: &nbsp;Welcome, everyone, from the
U.S. Fish and Wildlife Service’s National

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Conservation Training Center in Shepherdstown,
West Virginia.

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My name is John Ossanna and I would like to
welcome you to our webinar series held in

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partnership with the U.S. Geological Survey's
National Climate Change and Wildlife Science

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Center.

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Today's webinar is titled "What is Ecological
Drought?"

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We'll be exploring the impacts on natural
and cultural resources.

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We're excited to have Shawn Carter and Laura
Thompson with us, who are with the USGS National

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Climate Change and Wildlife Science Center,
as well as Shelley Crausbay with us today.

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Let's get started.

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To start things off, please join me in welcoming
Emily Fort, who's with the USGS.

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She'll be introducing our speakers today.

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Emily?

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Emily Fort: &nbsp;Hi, thanks, John.

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It's my pleasure to introduce Shawn Carter
and Laura Thompson from the USGS National

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Climate Change and Wildlife Science Center
in Reston, Virginia.

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Shawn is the senior scientist for our center
and works with the USGS offices and the DOI

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Climate Science Centers.

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Laura is a research ecologist.

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Shelley Crausbay is a postdoc for the National
Center for ecological analysis and synthesis

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at the University of California Santa Barbara.

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There, she is part of the Science for Nature
and People Partnership working program on

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ecological drought that was initiated by the
National Climate Change and Wildlife Science

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Center.

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She sits in Fort Collins, Colorado with the
North Central Climate Science Center.

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With that, I'm going to turn it over to Shawn.

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Shawn Carter: &nbsp;Thanks, Emily.

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Good afternoon, everyone.

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Thanks for joining us today for our kickoff
webinar on ecological drought.

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This is the first installment of a yearlong
series focused on the ecological consequences

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of drought across the country, within the
context of climate change and other stressors.

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The purpose of our talk today is to provide
some initial context and framing of ecological

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drought, or ecodrought, as we call it.

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Some justification for calling it out as its
own research initiative, which we've attempted

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to do, and also introduce some National Climate
Change and Wildlife Science Center sponsored

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projects.

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If you hear me say “nic-wisk”, I'm talking
about NCCWSC.

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It's just the shorthand that we use.

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After my brief comments, I'll pass the baton
to Shelley.

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She's one of our two postdoctoral researchers
helping us lead in the ecological drought

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working group.

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As Emily had mentioned, it's part of the Science
for Nature and People Partnership, or SNAPP,

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based at NCEAS in Santa Barbara.

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Shelley will outline our proposed conceptual
framework for ecodrought, and describe some

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pilot work assessing vulnerability being conducted
in the upper Missouri Headwaters region in

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Montana.

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Next, Laura will talk about some relevant
research projects to further illustrate the

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management implications of ecodrought.

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Some of which will be covered in more detail
on future webinars.

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Finally, I'll close out the webinar by covering
some of our national synthesis, and science

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communication efforts, and then we'll open
things up for questions.

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To reiterate just a little bit, we're here
today to talk about a subset of drought impacts.

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Those related to flora, fauna, and ecosystems,
and both managed and unmanaged systems.

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In fact, the genesis of this initiative was
based on management need.

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Resource managers were being told that climate
change will be increasingly impacting seasonal

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and annual, even decadal water availability,
and we're struggling to form adaptation plans

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that could help them plan for the future.

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How and when will ecosystems be transformed?

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Will conversions be temporary, or irreversible?

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How will other anthropogenic stressors interact
with drought?

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How prepared are systems currently to adapt
to climate change induced drought?

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We started this initiative to begin answering
some of these questions.

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As I mentioned, we hope to highlight how we're
addressing these questions throughout this

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series, throughout the year.

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To give a little bit more introduction to
the concept, is Shelley Crausbay, and I'll

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just hand it over to Shelley.

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Shelley Crausbay: &nbsp;Thank you, Shawn.

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I wanted to start briefly by telling you all
a little bit about SNAPP, the Science for

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Nature and People Partnership.

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SNAPP is the partnership among NCEAS, the
Wildlife Conservation Society, and the Nature

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Conservancy.

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What SNAPP does, is they host working groups
that really bring together scientists, practitioners,

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and policy makers, so that they can focus
on questions, mostly questions that are really

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at the nexus of biodiversity conservation,
human wellbeing, and economic development.

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All of the work that I'm presenting today
is a product of the ecological drought working

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group.

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This is our really diverse group of nearly
20 folks who are focused on this issue.

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In particular, I want to acknowledge, and
call out the core group, so the PIs, Shawn,

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who you just heard from, Molly Cross with
WCS, Kim Hall with TNC, and also, especially,

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Aaron Ramirez, the other postdoc on this project.

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Our group formed because ecosystems are more
vulnerable to 21st century droughts, but risks

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to ecosystems are not always considered in
drought planning and management.

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Our charge was to synthesize all the best
available science, and come up with a new

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conceptual framework that defines ecological
drought, parses out the national and human

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drivers, and really helps us identify important
tradeoffs, and perhaps some mutually beneficial

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solutions so that we can help mitigate effects,
and hopefully improve drought preparedness.

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Our group started simply by trying to define
ecological drought what is it?

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What I'm showing you here is a word cloud
of all the definitions that were put forward

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by our working group members.

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What we settled on was this definition here,
which is, an episodic deficit in water availability

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that drives ecosystems beyond thresholds of
vulnerability, impacts ecosystem services,

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and triggers feedbacks in natural and human
systems.

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To come up with a conceptual framework for
ecological drought, we are using a vulnerability

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framework where one dimension really looks
at each of those pieces of vulnerability,

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so exposure, sensitivity, and adaptive capacity,
on through to impacts.

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A really important second dimension really
tries to highlight both natural and human

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processes that go into this.

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Here's our framework for ecological drought,
our conceptual framework, and you can see

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that we're looking at all the pieces of vulnerability
from top to bottom.

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You see a box for exposure, for sensitivity
and adaptive capacity, and then a box for

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impacts, then you can see also from left to
right we're considering natural processes

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in yellow, and human processes in blue.

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Don't worry about trying to digest this conceptual
figure right now.

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I'm going to walk you through each piece of
it as we go along.

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First, I want to start with the top piece,
exposure.

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Looking on the yellow side, on the natural
side, we think about meteorological drought.

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Maybe this is the most easy thing for us to
think about when we think about drought, and

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particularly how meteorological drought is
propagated across the landscape via soils,

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the physiography, and landscape position,
and things like that.

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But the human side of exposure is also really
really important.

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For example, it starts with anthropogenic
climate change.

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Here, you see a map that's showing the percent
change in current versus year 2100 drought

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levels, and this is assessed with a pretty
common drought index called the PDSI.

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I just want to point out where, if you can
see the black stipples in this map, that's

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showing you where there's really strong model
agreement among all the CMIP5 models.

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Climate change is adding heat to the climate
system, and we know that heat is going into

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drying.

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While climate change may not necessarily manufacture
droughts, it's certainly going to exacerbate

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them.

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Another feature of anthropogenic climate change
is that climate change is increasing the risk

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of mega drought, so you can see on the left,
we're looking at the Central Plains.

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The Y axis is showing you the percent risk.

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From the last part of the past century, risk
was fairly low in the Central Plains, and

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here we're looking at three drought indices
PDSI and two soil moisture proxies.

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You look on the right side of that graph from
2050 to 2099 and you can see that that risk

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of a multidecadal drought is really strong.

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If you look at the map on the right side,
you can see the spatial variability in that

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risk, and you can see that the western US
and southern US is fairly at risk from mega

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drought in the future, but take a look at
that map and you can see that this really

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is truly a global issue.

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The other side of the human piece for exposure
is human water use.

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Humans really add to the severity of drought.

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You can see in this graph, this is just a
graph of water level in a particular basin,

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and you can see on the left, that's a totally
climateinduced drought where water level declines.

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In the middle, you can see an example of a
totally humaninduced drought where, let's

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say, water level declines solely because humans
are pulling water out of the system through

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irrigation or what have you.

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In reality, what we have is on the right.

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It's a combination of these things.

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For example, we can simulate a natural drought
shown there in yellow, but the reality of

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what we see and what we observe is a combination
of natural and human effects.

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In fact, in the future, human modifications
are set to reduce water availability perhaps

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even more than climate change in some regions,
for example the Colorado Basin where I live.

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All those pieces sum up our exposure piece
for ecological drought and we're calling that

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"ecologically available water," the idea that
this is a combination of these atmospheric

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and terrestrial water availability as well
as the natural and human processes that control

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that availability.

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Moving further down our conceptual diagram,
you can see we're thinking about sensitivity

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and adaptive capacity.

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These are just the ecological or evolutionary
characteristics of a system that control how

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strongly it responds to the same level of
exposure.

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Of course on the blue side, the human side,
natural resource management can certainly

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manipulate the ecological and evolutionary
characteristics that go into sensitivity.

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For example, the graph on the left, I'm showing
you a graph of predawn water potential for

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two different tree species in the Southwest.

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You can see that pinyon pine up top in red
had a much higher threshold by which once

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you cross that predawn water potential, you
are more likely to die whereas the juniper

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below that had a much lower threshold.

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The pinyon pines experienced much more mortality
than the junipers did.

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On the right side, we're showing this natural
resource management idea and how they can

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affect these ecological characteristics.

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For example, this graph is showing a time
series of basal area, and the yellow box in

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the middle is a strong drought that this site
experienced.

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You can see that the areas that rescind, that
top dotted line graph, really recovered much

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more quickly.

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Their basal area was much higher post drought
than the other sites.

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Moving down our conceptual figure further,
once you cross a threshold of vulnerability,

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you're going to get an ecological impact,
so, widespread tree mortality, major fish

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kills, things like that.

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In turn, that is going to cause losses perhaps
in ecosystem services that we see on the right

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side there in blue, but panning out overall
for our ecological drought conceptual framework,

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we think that the feedbacks are very important.

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This is represented by the arrows that you
see on either side of the graph.

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For example, on the yellow side, when an ecological
impact happens, let's say widespread tree

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mortality, that's now going to feedback and
change the ecological characteristics of that

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place, or it's going to change the landscape
characteristics say from the perspective of

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a species that's now migrated to a new location.

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Even through teleconnections, it can affect
the probability of future drought in that

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area.

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On the blue side, our idea is that once an
ecosystem service impact is so strong, it's

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going to feedback and cause humans to really
think about various institutions and how can

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we change our natural resource management
practices or our water use institutions in

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order to reduce vulnerability to these ecological
impacts in the future.

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At this point, we're trying to take our conceptual
framework and turn it into a really flexible

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framework for a vulnerability analysis.

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To do this, we're borrowing ideas from the
species and habitat distribution modeling

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community where essentially we're trying to
look at an ecological response, say tree mortality,

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and create models that drive that response
based on each aspect of our conceptual diagram.

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We're trying to integrate each aspect of vulnerability
and mostly we're trying to parse out which

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are the strongest drivers, these human or
natural controls on these responses.

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In particular, we want to discover what those
drivers are so that we can link them to particular

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strategies and outcomes that might reduce
vulnerability to ecological drought in the

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future.

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Essentially, this is what we're trying do.

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We're trying to come up with an equation for
ecological drought.

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For example, I'm pulling the icon from our
conceptual figure here.

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You can see on the left, we're looking at
some ecological response, say tree mortality

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as a function of a combination of meteorological
drought, landscape characteristics, climate

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change, water use, these ecological and evolutionary
characteristics, as well as resource management.

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Ok so let's see.

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Thinking about trying to come up with a function
to describe what drives a past ecological

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drought impact.

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Let's say your model was driven solely, or
really most importantly by soil moisture,

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or some aspect of the landscape characteristics,
like I have highlighted here.

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That might tell you, "Hey!

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Mimicking beaver activity is a really good
strategy to consider, and we need to really

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attempt to improve water retention on the
landscape."

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In contrast, you might have a system where
your primary driver was something about water

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infrastructure.

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Let's say you're modeling a fish kill, and
what you see is that it's really the timing,

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and amount of irrigation that was pulled out
of the system that maybe drove that impact.

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Then you might consider water markets as a
strategy, and really your desired outcome

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would be to lower that water withdraw.

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Another example might be a situation where
you're looking at tree mortality, and you

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see that it was actually plant density that
was a really strong driver of any kind of

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spatial variability in an ecological response.

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That might point to a strategy such as forest
thinning, so that you can reduce competition

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for water in the future.

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We're attempting to try and do this kind of
analysis in such a way that it's an easy template

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that can be shopped around to different areas,
different regions by using the same system.

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We're really excited to use software developed
by folks at the USGS Fort, and the USGS North

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Central Climate Science Center, and this is
the VisTrails Software for Assisted Habitat

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Modeling.

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This is an open source management and workflow
system.

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What's really great about it, is it builds
ecological response models using a bunch of

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different techniques.

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It's combining machine learning, and correlative
niche modeling.

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We think this is a really great framework
for us to do our analysis here, and hope that

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others can easily pick it up in the future.

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To test this out, we're working with the National
Drought Resilience Partnership, and they have

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a demonstration project in the upper Missouri
Headwaters region, which you can see here

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in this map, in Southwestern Montana right
along the Missouri River.

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What we're attempting to do is look at tree
mortality after an early 2000's really strong

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drought that was in this area, and essentially,
just following along with the functions, we're

00:17:51.341 --> 00:17:57.250
trying to look at tree mortality as a function
of rainfall, vapor pressure deficit, ecologically

00:17:57.250 --> 00:18:03.559
relevant landforms, and temperature, especially
including maximum temperatures, irrigation

00:18:03.559 --> 00:18:09.930
levels, any kind of human influence on stream
flow, as well as vegetation density, and identity.

00:18:09.930 --> 00:18:15.070
Hopefully any kind of maps that we can pull
together for resource management that has

00:18:15.070 --> 00:18:18.050
gone on in the area.

00:18:18.050 --> 00:18:23.290
We're hoping that this lays the groundwork,
and it really forms a template for other ecosystems

00:18:23.290 --> 00:18:24.880
and locations.

00:18:24.880 --> 00:18:29.670
We think that once we build these models,
you can automatically have a predictive system

00:18:29.670 --> 00:18:33.580
that could perhaps be an early warning for
ecological impacts.

00:18:33.580 --> 00:18:38.270
Not an early warning for drought, but an early
warning for those ecological impacts.

00:18:38.270 --> 00:18:41.600
The system could also allow you to test scenarios.

00:18:41.600 --> 00:18:46.700
So, for example, you could look at drought
impacts during future climates, or perhaps,

00:18:46.700 --> 00:18:52.010
and this is something I'm most excited about,
is how can we test the efficacy of different

00:18:52.010 --> 00:18:54.050
strategies.

00:18:54.050 --> 00:19:00.230
If you really think beaver mimicry is a great
idea, let's get some data layers developed

00:19:00.230 --> 00:19:05.929
for beaver activity, and we could put those
into our models, and see, "Well, how would

00:19:05.929 --> 00:19:11.270
tree mortality...How much would it have decreased
had we had this strategy on the landscape

00:19:11.270 --> 00:19:15.179
at the time?"

00:19:15.179 --> 00:19:21.270
With that, I wanted to say that we're really
excited about our new framework, and this

00:19:21.270 --> 00:19:26.270
template for analysis, and we're hopeful that
this framework and template could be used

00:19:26.270 --> 00:19:29.470
in upcoming USGS drought projects.

00:19:29.470 --> 00:19:33.230
With that, I would like to pass the baton
to Laura Thompson.

00:19:33.230 --> 00:19:36.430
Laura Thompson: &nbsp;Thank you, Shelley.

00:19:36.430 --> 00:19:49.179
Now, I'm going to talk about some of the ecological
drought projects that the NCCWSC is sponsoring.

00:19:49.179 --> 00:19:53.490
There's two different types of projects.

00:19:53.490 --> 00:19:57.330
We have a group of solicited projects, and
then a group of directed projects.

00:19:57.330 --> 00:20:05.060
The goal of both of these different studies
is essentially to fill key knowledge gaps

00:20:05.060 --> 00:20:13.630
with regards to ecological drought, and then
also to gain insight on future research that

00:20:13.630 --> 00:20:17.460
needs to come about of the results of these
knowledge gaps.

00:20:17.460 --> 00:20:29.780
In 2015, the NCCWSC put out a call for research
funding proposals.

00:20:29.780 --> 00:20:35.980
We ended up funding four different projects,
including drought related to forest management,

00:20:35.980 --> 00:20:46.490
drought and the impacts on migratory water
birds, and the impacts of drought on stream

00:20:46.490 --> 00:20:52.970
drying, as well as dryland ecosystems in the
Western US that include a lot of grassland

00:20:52.970 --> 00:20:53.970
areas.

00:20:53.970 --> 00:21:01.970
Just to go into a little bit of depth on some
of the findings on some of these projects,

00:21:01.970 --> 00:21:10.260
a recent study by Munson and Long…the goal
of the project was to better understand the

00:21:10.260 --> 00:21:14.330
resilience of grasslands under future climate
conditions.

00:21:14.330 --> 00:21:20.510
Grasslands are really important for providing
ecosystem services for a large portion of

00:21:20.510 --> 00:21:21.510
the US.

00:21:21.510 --> 00:21:28.880
The actual goal of the study was to determine
the capacity of grass species to shift phenology

00:21:28.880 --> 00:21:32.610
in response to climate over the last century.

00:21:32.610 --> 00:21:38.390
The approach that the authors took was to
use ovarian samples from approximately the

00:21:38.390 --> 00:21:42.400
last 100 years from several different regions
in the Western US.

00:21:42.400 --> 00:21:49.170
The colored areas are different eco regions,
the dots represent species locations, and

00:21:49.170 --> 00:21:54.650
the different colors represent different species.

00:21:54.650 --> 00:22:02.920
They were able to relate flowering times with
different climate variables.

00:22:02.920 --> 00:22:14.190
Just to give you an example, this graph shows,
on the left, two graphs show a species in

00:22:14.190 --> 00:22:19.720
relation to flowering date related to temperatures
through time, and temperature through space.

00:22:19.720 --> 00:22:31.090
Particularly on the bottom left graph, you
notice that species tend to either increase,

00:22:31.090 --> 00:22:38.870
advance their flowering date with relation
to temperature, or their flowering date becomes

00:22:38.870 --> 00:22:41.900
later as a result of temperature.

00:22:41.900 --> 00:22:49.530
When those are broken up by different photosynthetic
pathways and functional traits, we notice

00:22:49.530 --> 00:22:58.650
that C3 grasses, which are grasses that essentially
do better in cooler, wetter environment, tend

00:22:58.650 --> 00:23:04.220
to advance their flowering date in relation
to increases in temperature.

00:23:04.220 --> 00:23:10.460
Where C4 grasses that respond better to warmer,
dryer temperatures actually have later flowering

00:23:10.460 --> 00:23:11.730
date.

00:23:11.730 --> 00:23:18.240
The authors actually went a little further,
and these graphs just show individual species.

00:23:18.240 --> 00:23:25.429
Indian rice grass in the two left graphs,
and blue grama in the two right graphs.

00:23:25.429 --> 00:23:33.370
They found that the Indian rice grass is a
C3 grass, and will actually advance its flowering

00:23:33.370 --> 00:23:39.340
date if it's more pronounced in more Northern
eco regions.

00:23:39.340 --> 00:23:46.860
The further North you go, you may see a stronger
phenological response.

00:23:46.860 --> 00:23:52.620
The key findings from this study is that,
in the past, many grassland species have been

00:23:52.620 --> 00:23:55.970
responsive, phenologically, to climate, which
suggestw that that could continue in the future.

00:23:55.970 --> 00:24:00.730
Some of these systems may be fairly resilient
to climate change.

00:24:00.730 --> 00:24:09.370
It's not all doom and gloom, which is always
a good thing.

00:24:09.370 --> 00:24:15.350
To highlight some of our directed projects,
we have a number of studies on ungulates,

00:24:15.350 --> 00:24:25.600
including a couple of projects on bighorn
sheep, mule deer phenology, tracking how mule

00:24:25.600 --> 00:24:33.730
deer track green up throughout the season,
and a remote sensing project that is closely

00:24:33.730 --> 00:24:36.340
related to that, through EROS.

00:24:36.340 --> 00:24:47.200
Also, we have some fish projects and aquatic
projects in various places in the country.

00:24:47.200 --> 00:24:59.179
To highlight one of these studies in the Southwest,
the pronghorn is a species found in the Central

00:24:59.179 --> 00:25:03.740
North America, the interior Western US.

00:25:03.740 --> 00:25:10.970
The goal of this study was to better steer
conservation, sustainable conservation for

00:25:10.970 --> 00:25:19.070
ungulate species under climate change, and
then disentangle some of these relationships

00:25:19.070 --> 00:25:26.570
between climate, population dynamics, and
project them across time.

00:25:26.570 --> 00:25:32.450
This map shows the number of populations that
were included in this study.

00:25:32.450 --> 00:25:33.559
There were population surveys.

00:25:33.559 --> 00:25:41.540
This is 18 different populations in the Southwest,
and these population surveys go back to the

00:25:41.540 --> 00:25:43.090
'60s.

00:25:43.090 --> 00:25:52.309
They were able to relate population growth
with climate variables, and the authors found

00:25:52.309 --> 00:26:00.070
a pretty strong relationship between precipitation
for the majority of the population as well

00:26:00.070 --> 00:26:02.860
as temperature.

00:26:02.860 --> 00:26:10.750
The precipitation in particular had a strong
seasonal response, which suggests that precipitation

00:26:10.750 --> 00:26:14.490
was particularly important during the lactation
period for these animals.

00:26:14.490 --> 00:26:22.200
They wanted to be able to determine how these
animals might persist in the future given

00:26:22.200 --> 00:26:24.630
future climate scenarios.

00:26:24.630 --> 00:26:32.770
They were able to model using two different
climate scenarios from CMIP5, a less conservative

00:26:32.770 --> 00:26:46.780
or somewhat high scenario as far as greater
climate change impacts and more conservative

00:26:46.780 --> 00:26:51.710
estimates of slower climate change impacts.

00:26:51.710 --> 00:26:56.520
The black is the high scenario, and the gray
line is the low scenario.

00:26:56.520 --> 00:27:03.380
They essentially found that approximately
half the population will go extinct by the

00:27:03.380 --> 00:27:05.790
year 2090 in these different regions.

00:27:05.790 --> 00:27:19.430
In a few areas some of the populations might
actually be able to persist where precipitation

00:27:19.430 --> 00:27:28.130
may potentially increase.

00:27:28.130 --> 00:27:44.220
I mentioned we had some fish projects as well.

00:27:44.220 --> 00:27:54.350
One is in the southwestern US on the cutthroat
trout which is the most southern of the cutthroat

00:27:54.350 --> 00:27:55.350
species.

00:27:55.350 --> 00:28:01.260
There's several expectations with regards
to potential impacts of climate change, and

00:28:01.260 --> 00:28:04.700
very little monitoring has occurred for this
species.

00:28:04.700 --> 00:28:10.510
The goal was to examine potential drought
risks for these vulnerable populations.

00:28:10.510 --> 00:28:18.549
I apologize the picture is covering it up,
but you have a pretty picture of a trout,

00:28:18.549 --> 00:28:25.419
and you can see the orange cutthroat on the
front.

00:28:25.419 --> 00:28:29.630
The approach was to empirically access the
effects of seasonal stream temperatures and

00:28:29.630 --> 00:28:33.750
discharge in Rio Grande cutthroat trout that
may be potentially at risk for drought conditions,

00:28:33.750 --> 00:28:47.179
and then model drought effects on the persistence
of populations including modeling stream discharge,

00:28:47.179 --> 00:28:54.090
intermittency, and temperature in these different
streams where they exist.

00:28:54.090 --> 00:29:04.800
Finally evaluate how drought conditions will
alter population model rates.

00:29:04.800 --> 00:29:10.789
We have a study that's just starting up in
Hawai’i.

00:29:10.789 --> 00:29:13.361
Drought doesn't just occur in the southwest.

00:29:13.361 --> 00:29:16.110
We actually do have island drought as well.

00:29:16.110 --> 00:29:19.170
The need for this particular study is due
to the fact that there's limited incorporation

00:29:19.170 --> 00:29:20.870
of climate change into stream management.

00:29:20.870 --> 00:29:27.370
There is a desire to better understand future
conditions.

00:29:27.370 --> 00:29:40.920
The goal of this project is to identify critical
conservation areas with climate change using

00:29:40.920 --> 00:29:42.720
stream flow.

00:29:42.720 --> 00:29:48.580
The approach is to simulate stream flow, both
windward and leeward watersheds and access

00:29:48.580 --> 00:29:52.010
the impact of changes in climate on native
species; describe current habitat usage and

00:29:52.010 --> 00:29:58.940
project future distribution of these species
and then build an assessment framework called

00:29:58.940 --> 00:30:06.990
“ridge to reef” framework for prioritizing
aquatic conservation efforts.

00:30:06.990 --> 00:30:14.669
And then also compile stream conditions and
information on species distribution.

00:30:14.669 --> 00:30:21.870
This provides a bit of an overview of some
of our solicited and directed research projects.

00:30:21.870 --> 00:30:29.360
Most of these I should point going back to
Shelley's framework tend to focus more on

00:30:29.360 --> 00:30:38.730
the ecological impacts that certainly have
implications for natural resources management

00:30:38.730 --> 00:30:40.200
and ecosystem services.

00:30:40.200 --> 00:30:43.910
I'm going to hand it back to Shawn Carter.

00:30:43.910 --> 00:30:46.290
Shawn: &nbsp;Thanks, Laura.

00:30:46.290 --> 00:30:53.530
As Laura alluded to there is socioeconomic
component to some of this work that we're

00:30:53.530 --> 00:30:59.440
not addressing given time constraints today
but will be dealt with in future webinars

00:30:59.440 --> 00:31:01.539
as part of the SNAPP initiative.

00:31:01.539 --> 00:31:06.770
Finally, I would like to close today's presentation
by mentioning two other activities that are

00:31:06.770 --> 00:31:10.820
meant to summarize our understanding of eco
drought and the implications for research

00:31:10.820 --> 00:31:15.520
management and broader public understanding.

00:31:15.520 --> 00:31:19.450
First in cooperation with the Integration
and Application Network team at the University

00:31:19.450 --> 00:31:24.990
of Maryland, we're holding a series of regional
workshops to conceptualize ecological drought

00:31:24.990 --> 00:31:26.880
impacts around the country.

00:31:26.880 --> 00:31:32.419
These are the impacts encountered by each
of our eight Department of Interior Climate

00:31:32.419 --> 00:31:33.730
Science Centers.

00:31:33.730 --> 00:31:36.559
They're shown here on the map.

00:31:36.559 --> 00:31:40.919
Our goal is to engage scientists and managers
in discussions about how future droughts might

00:31:40.919 --> 00:31:43.660
play out within the respective geographies.

00:31:43.660 --> 00:31:51.289
So far we've completed five of the eight CSCs
with each producing its own summary newsletter

00:31:51.289 --> 00:31:53.460
which are shown here.

00:31:53.460 --> 00:31:57.880
Additional materials can be found using the
links that I'm going to provide at the end

00:31:57.880 --> 00:32:00.409
of this talk.

00:32:00.409 --> 00:32:05.650
Finally, we hope to integrate all of these
activities that we've just touched on in this

00:32:05.650 --> 00:32:07.910
webinar today.

00:32:07.910 --> 00:32:12.230
Our proposed framework for using ecologically
available water and integrating some of those

00:32:12.230 --> 00:32:17.350
feedbacks that Shelley mentioned, our SNAPP
pilots in the upper Missouri, working with

00:32:17.350 --> 00:32:23.419
our partners in the National Drought Resilience
Partnership, our sponsored research from around

00:32:23.419 --> 00:32:29.370
the country and then our regional conceptualizations
of ecological drought from these workshops

00:32:29.370 --> 00:32:31.530
at our Climate Science Centers.

00:32:31.530 --> 00:32:36.170
We hope to incorporate all of these into a
comprehensive synthesis over the summer, a

00:32:36.170 --> 00:32:39.020
national synthesis of ecological drought.

00:32:39.020 --> 00:32:44.290
Stay tuned for a more national scale summary
of these projects in the future.

00:32:44.290 --> 00:32:48.690
With that, I'll conclude our presentation
today.

00:32:48.690 --> 00:32:54.120
Listed here are a few sources for more information
and also some acknowledgement of the valuable

00:32:54.120 --> 00:32:56.890
contributions from our partners who we've
mentioned.

00:32:56.890 --> 00:33:00.040
I'd like to thank you all very much for your
time today.

00:33:00.040 --> 00:33:05.880
I apologize in advance that we won't be able
to accommodate everybody that wanted to join.

00:33:05.880 --> 00:33:08.000
We'll entertain your questions.

00:33:08.000 --> 00:33:09.250
Thanks.

00:33:09.250 --> 00:33:12.830
John: &nbsp;Thank you all for your presentations.

00:33:12.830 --> 00:33:15.059
First off, let's start with Evan Albert.

00:33:15.059 --> 00:33:17.250
Could this be part of a historical cyclical
phenomenon?

00:33:17.250 --> 00:33:20.730
I read somewhere that analysis of tree rings
suggest the western states have had many droughts

00:33:20.730 --> 00:33:26.250
of two decades or longer including two mega
droughts lasting longer than 100 years.

00:33:26.250 --> 00:33:33.570
Do you know what that was in reference to?

00:33:33.570 --> 00:33:37.419
I'm sorry about that.

00:33:37.419 --> 00:33:42.210
Shelley: &nbsp;I think Evan's question is about
megadrought.

00:33:42.210 --> 00:33:45.000
I'm going to guess.

00:33:45.000 --> 00:33:49.310
Evan, this is a really active area of research
right now.

00:33:49.310 --> 00:33:54.280
There's a lot of really cool stuff going,
and it's true there were lots of mega droughts

00:33:54.280 --> 00:33:59.270
in the past particularly in the southwest
and particularly during the medieval climate

00:33:59.270 --> 00:34:03.780
anomaly, so around 1,000 years ago right before
the little ice age.

00:34:03.780 --> 00:34:09.419
There's a lot of thought around whether those
higher temperatures during that time period

00:34:09.419 --> 00:34:13.450
drove those mega droughts, but it's a really
complex picture.

00:34:13.450 --> 00:34:18.079
There's a lot involved with sea surface temperatures,
with various oscillations like the Pacific

00:34:18.079 --> 00:34:23.899
decadal oscillation or the AMO, things like
that, internal atmospheric feedbacks are really

00:34:23.899 --> 00:34:26.169
important.

00:34:26.169 --> 00:34:30.289
One thing I'd say is that maybe there isn't
a whole lot of really strong consensus right

00:34:30.289 --> 00:34:34.859
now, but it's a really active area of research
where a lot of people are doing great work

00:34:34.859 --> 00:34:41.599
to try and figure out what really drove megadroughts
in the past, and what are we likely to see

00:34:41.599 --> 00:34:44.629
in the future.

00:34:44.629 --> 00:34:55.710
John: &nbsp;Would it be possible for all citations
and papers used for these presentations to

00:34:55.710 --> 00:34:58.260
be summarized for us?

00:34:58.260 --> 00:34:59.260
Certainly.

00:34:59.260 --> 00:35:07.690
If the presenters are willing to come up with
something, I could certainly pass that along

00:35:07.690 --> 00:35:13.960
to everyone that would be interested.

00:35:13.960 --> 00:35:18.269
Shelley or Shawn or Laura, would any of you
be interested in that?

00:35:18.269 --> 00:35:21.339
Shelley: &nbsp;Yeah, absolutely.

00:35:21.339 --> 00:35:22.339
Happy to do that.

00:35:22.339 --> 00:35:28.700
John: &nbsp;Whenever they get it to me I'd be
happy to forward that on to everyone else.

00:35:28.700 --> 00:35:31.079
Shelley: &nbsp;Thanks, John.

00:35:31.079 --> 00:35:33.450
John: &nbsp;Roger Sayre.

00:35:33.450 --> 00:35:38.210
I'm hoping I say that right.

00:35:38.210 --> 00:35:43.309
Will the Hawaii work and ecological stream
classification that NCCWSC has reported as

00:35:43.309 --> 00:35:44.690
a stratification device?

00:35:44.690 --> 00:35:53.619
Shawn: &nbsp;I'm looking at the person who might
be responsible in our office for that.

00:35:53.619 --> 00:35:59.740
We don't have an answer for Roger at this
moment, but that is an active area of research

00:35:59.740 --> 00:36:04.739
as well that we have a couple of investigators
working on right now.

00:36:04.739 --> 00:36:06.289
Stay tuned.

00:36:06.289 --> 00:36:13.369
Actually, I'll just add that is one of the
Climate Science Centers that has not had their

00:36:13.369 --> 00:36:18.670
drought workshop yet, and we'll be holding
that in about four to six weeks from now.

00:36:18.670 --> 00:36:21.239
That will also be discussed at that workshop.

00:36:21.239 --> 00:36:23.210
John: &nbsp;Doug Beard.

00:36:23.210 --> 00:36:27.819
The Hawai’i work is Ralph Tingley’s work.

00:36:27.819 --> 00:36:31.759
Uncertain how it'd be used yet.

00:36:31.759 --> 00:36:32.759
OK.

00:36:32.759 --> 00:36:38.619
Thank you for adding onto that as well, Doug.

00:36:38.619 --> 00:36:48.640
Monica Ketcham is uploading some links on
ecological drought from NCCWSC and SNAPP.

00:36:48.640 --> 00:36:50.069
Thank you, Monica.

00:36:50.069 --> 00:36:54.470
Feel free to take advantage of those anyone
who is attending.

00:36:54.470 --> 00:37:03.430
I would like to thank Shawn and Laura and
Shelley and Kate and Elda and everyone that

00:37:03.430 --> 00:37:04.499
put this together.

00:37:04.499 --> 00:37:07.789
It was quite a few people in this presentation.

00:37:07.789 --> 00:37:11.900
I would like to thank all of you for your
presentation.

00:37:11.900 --> 00:37:15.420
I'd like to thank everyone who attended for
your participation in this.

00:37:15.420 --> 00:37:17.049
Shawn: &nbsp;Thank you.

00:37:17.049 --> 00:37:18.130
Shelley: &nbsp;Thanks.


