WEBVTT
Kind: captions
Language: en

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Ashley Fortune: �Good afternoon or good
morning from the U.S. Fish and Wildlife Service's

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National Conservation Training Center in Shepherdstown,
West Virginia.

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My name is Ashley Fortune, and I would like
to welcome you to today's broadcast of the

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NCCWSC's Climate Change Science and Management
Webinar Series.

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This series is held in partnership with the
U.S. Geological Survey's National Climate

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Change and Wildlife Science Center.

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Today's webinar will focus on the impacts
of melting glaciers on nutrient supply in

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coastal ecosystems of the northern Gulf of
Alaska.

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Our speaker today is Dr. John Crusius.

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John received a BA in Chemistry from Carleton
College and a PhD in Geochemistry from Columbia

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University and the LamontDoherty Earth Observatory.

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John did postdoctoral work at the University
of British Columbia in Vancouver and worked

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for a while as a research scientist at the
International Atomic Energy Agency Marine

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Environment Lab in Monaco.

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From 2003 to 2011, John was a research scientist
in Woods Hole at the USGS Coastal and Marine

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Geology Center.

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Since 2011, John has remained a USGS research
scientist with the Coastal and Marine Geology

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Program, but he is based in Seattle at the
University of Washington, where he has an

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affiliate faculty position in the School of
Oceanography.

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John is married and has one son in high school.

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John, that's quite the experience.

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Everyone, please welcome John, and you may
begin.

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Thank you.

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John Crusius: �Thanks a lot, Ashley, and
thanks for your help setting up.

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Good afternoon, everyone, or good morning,
depending on which time zone you're in.

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Today, I'd like to speak on "Impacts of Melting
Glaciers on Nutrient Supply and Coastal Ecosystems

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of the Northern Gulf of Alaska."

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I want to acknowledge a lot of collaborators
who did a lot of this work.

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I'm going to give a broad overview.

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I've listed a lot of people here.

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I don't have time to acknowledge them all
individually.

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In particular, I want to acknowledge funding
from the USGS National Climate Change and

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Wildlife Science Center, from the Coastal
Marine Geology Program, and from the Mendenhall

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Postdoctoral Fellowship Program.

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I'm going to speak briefly on some NASAfunded
work of ours that is relevant to the overall

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project.

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Here's an outline of what I want to present
today.

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This is a challenging talk because this is
a large, multiinvestigator study, and I'm

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trying to summarize what a lot of people did
in 45 minutes.

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Pretty much every slide I present could be
expanded into a 45 minute talk, so I'm going

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to try to cover a lot of ground.

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I'm also going to try to keep it accessible
to a fairly general audience while maintaining

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the scientific integrity, so please bear with
me.

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I'll try to keep you with me as I go.

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Just to give you an outline, I'm going to
speak briefly on the evidence for glacier

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mass loss, from the northern Gulf of Alaska
in particular.

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I'm going to examine the marine food web foundations,
including nutrients nitrate and iron, which

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limit phytoplankton growth.

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I hope I will convince you that glaciers are
a source of iron, which is a nutrient that

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limits phytoplankton growth and that rivers
and sediment resuspension and dust are all

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important sources of the micronutrient iron.

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I'm going to discuss some seasonal variability
in the nutrient sources and allude to the

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fact that there's hyperactivity in the spring
along the continental shelf transect that

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we studied in response to this high nutrient
supply.

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By late summer, nitrate is the limiting nutrient.

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Zooplankton and fish abundance tend to be
high in the river plume that we studied, the

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Copper River plume, for reasons of predator
evasion.

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Then I'm going to end with some model simulations
of Copper River discharge into the Gulf of

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Alaska, including some simulations of two
times present discharge and discuss some impacts

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of that.

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Here are some results from a recent paper
from the journal "Nature" showing evidence

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for glacier mass loss worldwide, although
I'm focusing strictly on the northern Gulf

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of Alaska area glaciers.

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Here's a map of North America that you'll
all recognize, and here's Alaska.

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You see this southern Alaska region at the
northern end of what we refer to as the Gulf

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of Alaska, this being the Gulf of Alaska right
where the number 12 is.

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This area is lined by many mountain glaciers,
and there's a paper, this paper that I mentioned

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in "Nature," which documented mass loss of
these glaciers over the time period 2003 to

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2011 using the GRACE Satellite.

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What you see here from 2003 to 2011 is mass
increasing in the winter, decreasing in the

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summer and that cycle repeating over and over
again, but there's a general downward trend

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that's pretty much indisputable over that
time frame.

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There have been a lot of high profile papers
on this general topic in recent years, and

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I could have picked any number of them.

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I picked this one mainly because it's quite
recent, it was in the journal "Nature," and

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it actually shows data from this southern
Alaska region.

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Some work that is relevant that was done by
one of our USGS team members, I'm presenting

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here.

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This is work done on the Bering Glacier from
2002 to 2012.

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Our project really included fieldwork only
from 2010 and 2011, so this represents a whole

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lot of extra effort by the lead author, Ed
Josberger.

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This is work from the Bering Glacier at the
northern end of the Gulf of Alaska.

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It's just a little bit east of the Copper
River, for those of you who know where that

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is, and I'll show you that in a minute.

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This is a little bit different from the last
paper I alluded to.

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This is documenting summer melt as a function
of time from 2002 to 2012, and it teases apart

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the contributions to that melt of ice melt,
snow melt, and precipitation.

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What's striking, to me anyway, is that there's
surprisingly little variability during this

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10year time frame, fairly steady melt of 40
plus or minus 3 cubic kilometers per year.

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A little bit of up and down as time goes on
but not a really noticeable temporal trend

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showing an increase over time.

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This line with the diamonds connecting it
shows melting degree days, a measure of the

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warmth, essentially, during the summer melt
period.

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Sure enough, during warmer periods, as you
might expect, there's more melt and less melt

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during colder days, but there is not an overall
trend.

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I want to emphasize that this is not really
in conflict with the previous slide because

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this is only showing the summer melt.

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This is not looking at the annual mass balance,
but interestingly, over this 10year time period,

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there's not an increase in melt over time.

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I'm going to come back to this analysis of
what might happen in the future a little bit

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later.

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This is a map, obviously, of North America,
primarily, and here is the Gulf of Alaska

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area.

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Here is this coastal Gulf of Alaska area.

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What I want to point out simply is that this
area, which is not that well known to most

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people living in the lower 48 states, despite
being fairly far removed from large population

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centers, it's actually an area that receives
a tremendous amount of river discharge.

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Just to give you a number, these coastal Gulf
of Alaska rivers discharge about 870 cubic

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kilometers per year.

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Contrast that with the Mississippi River,
a much better known river, which discharges

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530 cubic kilometers per year, and the Columbia
and the Yukon, around 200 cubic kilometers

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per year.

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Despite the fact that these Gulf of Alaska
rivers are relatively obscure to most people,

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they discharge a heck of a lot of water, and
that's because there's a lot of precipitation

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in this region.

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That's the main reason, primarily there's
a lot of precipitation and then much of that

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drains off into the Gulf of Alaska.

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Another reason this area is of interest, scientifically,
is that the Gulf of Alaska, again that's this

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region to the south of Alaska, is referred
to as an ironlimited ecosystem.

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That means that iron is a nutrient that limits
the growth of phytoplankton, essentially the

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base of the marine food web because of its
relative scarcity.

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What I'm showing here in this plot is a global
map of nitrate concentrations.

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What you see is that the nitrate concentrations
in this Gulf of Alaska region are fairly high.

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That's for a couple of reasons, really.

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It's partly because that's at the end of what's
casually referred to as the Global Conveyor

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Belt, the meridional overturning circulation
that leads to upwelling of deepwater in this

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north Pacific region.

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So, it's the end of the line in terms of oceanographic
circulation, but, in addition, phytoplankton

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growth is ironlimited because of distance
from iron sources in this region.

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That is another thing that makes it somewhat
unusual relative to the rest of the ocean,

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where nitrate is more typically the limiting
nutrient.

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We know that iron is a limiting nutrient,
but we don't know very much about the processes

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that transport iron to the ironlimited regions
of the Gulf of Alaska.

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Some of this work is going to shed some light
on some of those processes.

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This is just a twodimensional schematic that
doesn't really do justice to everything, and

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I just want to point out this does not show
eddies, which are a phenomenon that can transport

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iron from the coast into the open ocean.

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I'm going to focus on riverine inputs, on
dust inputs, on some iron inputs from this

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continental shelf region, and all of these
end up being sources of iron that fuel high

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plankton productivity in this shelf region.

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Another thing that makes this part of the
world interesting, this is again showing the

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southern Alaska region and the coastal area
just south of that glacierdominated area I

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referred to.

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This is a plot of chlorophyll concentration,
and you see this high chlorophyll concentration

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in this coastal area.

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Some work by Ware and Thomson in "Science"
in 2005 showed a relationship between mean

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chlorophyll concentration and the mean resident
fish yield, which they interpreted to mean

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this ecosystem was controlled from the bottom
up, in other words, from the base of the food

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web up, and phytoplankton being the base of
the food web.

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One of the questions we posed was whether
this ecosystem of the Copper River plume region,

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and that, just for your reference, is right
around here on this plot, is also controlled

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in similar bottomup ecosystem fashion.

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Why the Copper River?

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We're going to focus on the Copper River,
which is one of these rivers that drains into

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the Gulf of Alaska.

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First of all, it's the site of important fisheries.

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It's the single largest freshwater source
for the Gulf of Alaska.

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A significant portion of the Copper River
watershed is glaciercovered, and that has

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implications for the nutrient cycling and
nutrient inputs into the ocean.

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Also, prior to this work there were little
or no iron data and few oceanographic observations

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from the vicinity.

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Finally, a more general justification is that
river plumes, in other words, the plume of

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water that extends out into the ocean from
the river, can serve as protection for various

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organisms from predators.

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This is a plot of Copper River discharge from
the Million Dollar Bridge Station, not too

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far from where it discharges into the ocean.

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A bit of an unusual representation of time,
but the main point to make here is that...I

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guess there are a couple of main points.

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First of all, discharge increases dramatically
in this AprilMay time frame.

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Discharge reaches a peak in JulyAugust, and
it's still fairly high in the fall in response

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to various floods.

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This pattern of discharge is typical.

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This is an average discharge from the Copper
River.

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It's typical for this region.

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It's quite atypical for probably most of the
rivers that most of you who are listening

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are familiar with.

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The reason the discharge peaks in the summer
is not that that's when all the precipitation

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happens.

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It's because that's when all the snow and
ice melt happens, so you get this massive

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discharge peak in July and August.

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In the winter, from roughly November to March
or so, there's very little discharge.

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Again, there's plenty of precipitation.

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This is not evidence of lack of precipitation
at that time.

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It's just that the precipitation is freezing
and not going out the river.

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This timing is quite different from rivers
that many of you might be familiar with, but

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it has implications for the timing of the
nutrient inputs into the ocean in this part

00:14:58.350 --> 00:14:59.350
of the world.

00:14:59.350 --> 00:15:06.639
One of the first questions we posed was, "How
will the flux and distribution of riverine

00:15:06.639 --> 00:15:13.310
iron delivered to the Gulf of Alaska change
due to warming climates and retreating glaciers"?

00:15:13.310 --> 00:15:17.080
First of all, let's just get oriented here.

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We're going to show some data from a series
of tributaries from the Copper River watershed.

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Here's Alaska.

00:15:25.920 --> 00:15:33.019
Here, outlined in orange, is the Copper River
watershed, and I'm going to show data from

00:15:33.019 --> 00:15:34.690
the set of tributaries.

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This is work that was carried out virtually
entirely by Andrew Schroth as part of his

00:15:41.660 --> 00:15:48.319
Mendenhall Postdoctoral Program when he was
at Woods Hole.

00:15:48.319 --> 00:15:52.439
This is the Copper River watershed.

00:15:52.439 --> 00:15:57.160
I'm going to show data from a few different
river types, but the two main points I want

00:15:57.160 --> 00:16:00.140
to make are that there are these glacierdominated
rivers.

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Those of you who have seen glacierdominated
rivers have probably seen this type of murky

00:16:04.250 --> 00:16:07.089
water before, this murky gray water.

00:16:07.089 --> 00:16:11.779
It's murky and gray because there's a lot
of fine particulate matter in it that results

00:16:11.779 --> 00:16:15.120
from weathering from these glaciers.

00:16:15.120 --> 00:16:16.269
That's one river type.

00:16:16.269 --> 00:16:22.910
Whenever the river drains what we call a "glacierized
river valley," this is typically what you

00:16:22.910 --> 00:16:25.380
see, very murky water.

00:16:25.380 --> 00:16:31.970
The other river type is this boreal lowland
�blackwater� river type.

00:16:31.970 --> 00:16:41.870
This is a river that drains water that's much
lower elevation, no glaciers, but very peaty.

00:16:41.870 --> 00:16:49.509
It's a region that's full of peatlands, wetlands,
and, as a consequence, the water gets very

00:16:49.509 --> 00:16:55.220
brown because it has high concentrations of
organic acids, high dissolved organic matter

00:16:55.220 --> 00:16:56.220
concentrations.

00:16:56.220 --> 00:17:03.149
This is actually a photo that shows these
two river types mixing together when they

00:17:03.149 --> 00:17:08.939
flow into each other, just to show those two
river types in one photo.

00:17:08.939 --> 00:17:15.420
I'm going to show how each of these manifests
itself in terms of impacts on iron in just

00:17:15.420 --> 00:17:16.420
a minute.

00:17:16.420 --> 00:17:20.480
Here is a picture of the, again, the Copper
River watershed.

00:17:20.480 --> 00:17:25.600
These dots represent different tributaries
of the Copper River.

00:17:25.600 --> 00:17:31.390
Here's Andrew showing off his trace metal
clean river sampling strategy.

00:17:31.390 --> 00:17:35.110
We always get a lot of laughs when we show
this image of him in the truck.

00:17:35.110 --> 00:17:40.170
We need to get a different image for that,
but that shows the trace metal clean river

00:17:40.170 --> 00:17:41.170
sampling.

00:17:41.170 --> 00:17:47.440
We're going to mention some different size
fractions of iron.

00:17:47.440 --> 00:17:51.440
Particulate iron is larger than 0.45 micron.

00:17:51.440 --> 00:17:57.240
Colloidal iron is smaller than 0.45 micron
but larger than 0.02 micron, and dissolved

00:17:57.240 --> 00:17:59.930
is less than 0.02 micron.

00:17:59.930 --> 00:18:04.550
This has implications for the fate of that
iron as it goes into the ocean, which we'll

00:18:04.550 --> 00:18:06.870
get to in a minute.

00:18:06.870 --> 00:18:14.200
So these different tributary types have different
characteristics, the glacierized tributaries...Let

00:18:14.200 --> 00:18:20.740
me back up, I'm plotting colloidal iron.

00:18:20.740 --> 00:18:26.050
You can think of it as small particles, concentration
of small particles of iron versus dissolved

00:18:26.050 --> 00:18:27.050
iron.

00:18:27.050 --> 00:18:35.150
This is stuff that passes through a very fine
filter and it's truly in solution, truly dissolved.

00:18:35.150 --> 00:18:39.930
These two different river types have very
different iron types.

00:18:39.930 --> 00:18:47.260
There's the largely particulate iron that's
common in these glacierized watersheds and

00:18:47.260 --> 00:18:52.610
a largely dissolved iron in these wetland
dominated rivers.

00:18:52.610 --> 00:18:57.450
You can see that in a different way when you
plot colloidal iron versus colloidal silica.

00:18:57.450 --> 00:19:05.340
Essentially, the glacierdominated rivers have
both fine particulate iron and fine particulate

00:19:05.340 --> 00:19:08.470
silica because it's essentially ground-up
rock.

00:19:08.470 --> 00:19:12.790
There's ground-up rock that is giving it that
milky gray color.

00:19:12.790 --> 00:19:20.170
That's a source of iron, that's also a source
of dissolved silica, versus the boreal forested

00:19:20.170 --> 00:19:27.680
rivers which show much lower dissolved silica
concentration and, typically, smaller concentrations

00:19:27.680 --> 00:19:30.590
of iron as well.

00:19:30.590 --> 00:19:37.521
Andrew did some time series river sampling
that I don't have time to show, but I just

00:19:37.521 --> 00:19:40.760
want to acknowledge that that work is a big
part of this project as well.

00:19:40.760 --> 00:19:45.090
I'm going to jump ahead to some work that
Andrew and I did at the mouth of the Copper

00:19:45.090 --> 00:19:46.090
River.

00:19:46.090 --> 00:19:51.970
Here is a satellite image of the Copper River
and you see this muddy river plume extending

00:19:51.970 --> 00:19:54.420
into the ocean.

00:19:54.420 --> 00:19:59.490
On the right is actually a close up of that
taken with a camera.

00:19:59.490 --> 00:20:07.900
On the left is this muddy river plume, freshwater,
on the right is seawater, and this front occurs

00:20:07.900 --> 00:20:13.750
over a space of centimeters really, it's really
dramatic.

00:20:13.750 --> 00:20:19.010
What is known from the iron literature is
that dissolved iron tends to be removed in

00:20:19.010 --> 00:20:20.130
estuaries.

00:20:20.130 --> 00:20:26.070
Now, the estuary of the Copper River is quite
different from what most of you might be familiar

00:20:26.070 --> 00:20:29.230
with when you think of an estuary.

00:20:29.230 --> 00:20:34.930
The Copper River is more this abrupt front
from fresh to salt rather than a gradual mixing

00:20:34.930 --> 00:20:36.170
of the two.

00:20:36.170 --> 00:20:42.660
We did our best to try to sample across this
front and I'm going to focus first on this

00:20:42.660 --> 00:20:49.170
plot on the lower right where I'm plotting
dissolved iron versus salinity.

00:20:49.170 --> 00:20:52.210
The dissolved iron concentrations that have
low salinity are quite high.

00:20:52.210 --> 00:20:55.090
That's because of this fresh water input into
the ocean.

00:20:55.090 --> 00:21:00.350
At high salinity they're low, because that
iron is getting diluted with iron poor sea

00:21:00.350 --> 00:21:02.280
water.

00:21:02.280 --> 00:21:13.550
If you had mixing of freshwater with sea water
with no iron removal, the data points would

00:21:13.550 --> 00:21:18.690
fall on a line, looking something like this
for my pretty much a straight line.

00:21:18.690 --> 00:21:24.410
Instead what you see is this pronounced curve
where the iron concentration has dropped dramatically

00:21:24.410 --> 00:21:30.230
as you go into the salt water and then they
stay fairly low.

00:21:30.230 --> 00:21:35.510
That shape is characteristic of dissolved
iron removal.

00:21:35.510 --> 00:21:42.040
What happens is the organic iron complex readily
flocculates and is removed.

00:21:42.040 --> 00:21:50.870
What that means is iron from these lowland,
wetland dominated rivers is largely removed

00:21:50.870 --> 00:21:52.110
when it hits the ocean.

00:21:52.110 --> 00:21:58.650
By contrast, this total dissolvable iron is
a measure of the particulate iron.

00:21:58.650 --> 00:22:06.970
This iron concentration, also quite high,
shows different characteristics, it's largely

00:22:06.970 --> 00:22:13.200
a linear behavior between freshwater and saline
water.

00:22:13.200 --> 00:22:17.190
What that means is a lot of the particulate
iron in other words, a lot of the particulate

00:22:17.190 --> 00:22:22.140
iron is coming out from the glacier, this
muddy, gray stuff is actually getting mixed

00:22:22.140 --> 00:22:23.830
out into the ocean without a lot of removal.

00:22:23.830 --> 00:22:30.050
So that has some big implications, the fact
that that fine particulate stuff largely persists

00:22:30.050 --> 00:22:31.580
in the ocean.

00:22:31.580 --> 00:22:40.090
That's a very quick summary of the terrestrial
sampling, I'm going to show you a summary

00:22:40.090 --> 00:22:44.680
of the marine sampling that we did on this
transect from the Copper River mouth.

00:22:44.680 --> 00:22:46.260
Here is the Copper River.

00:22:46.260 --> 00:22:50.570
Again, here is Alaska, here's the mouth of
the Copper River.

00:22:50.570 --> 00:22:56.550
This is the continental shelf break, our transect
extended from the mouth of the Copper River

00:22:56.550 --> 00:22:59.740
out beyond the continental shelf break.

00:22:59.740 --> 00:23:04.960
We sampled on this ship, the RB Montague,
based out of Cordova, Alaska.

00:23:04.960 --> 00:23:08.790
I'm just going to quickly show you some trace
metal clean sampling equipment.

00:23:08.790 --> 00:23:20.010
We used this Teflon vein that was put in the
water, it houses Teflon line tubing.

00:23:20.010 --> 00:23:24.080
This thing here is submerged below the water.

00:23:24.080 --> 00:23:29.620
There's a pump on the ship that runs all the
time and sucks up water from this intake through

00:23:29.620 --> 00:23:34.350
the tubing, up through here, it comes into
this lab.

00:23:34.350 --> 00:23:39.551
Here's an inside shot of the lab and you see
this tubing coming to the lab.

00:23:39.551 --> 00:23:41.620
This is Andrew Schroth's sampling.

00:23:41.620 --> 00:23:49.550
Essentially, while the ship is moving, we
can sample trace metal clean water just by

00:23:49.550 --> 00:23:50.920
turning a tap.

00:23:50.920 --> 00:23:52.550
It's pretty cool.

00:23:52.550 --> 00:23:58.390
The time from sample intake to sample collection
is about one minute.

00:23:58.390 --> 00:24:00.250
It's quite a quick process.

00:24:00.250 --> 00:24:04.670
I'm going to show you some data from that
sample collection system, which is necessary,

00:24:04.670 --> 00:24:09.320
that I should point out, to collect uncontaminated
samples for iron.

00:24:09.320 --> 00:24:15.790
One thing about iron is it's easy to contaminate
when you're sampling from a big, rusty ship,

00:24:15.790 --> 00:24:18.290
because their concentrations are pretty low
in the ocean typically.

00:24:18.290 --> 00:24:23.110
This is some of the motivation for this marine
work.

00:24:23.110 --> 00:24:25.030
This is an image of chlorophyll.

00:24:25.030 --> 00:24:30.270
Here is Prince William Sound, to orient you,
here is the Copper River.

00:24:30.270 --> 00:24:31.270
Red is high chlorophyll.

00:24:31.270 --> 00:24:35.530
This is from May of 2009, which is actually
a year before our sampling started.

00:24:35.530 --> 00:24:39.701
But the main point here is there are these
high plumes of chlorophyll in this coastal

00:24:39.701 --> 00:24:45.530
region that respond, we think, to high concentrations
of nutrients.

00:24:45.530 --> 00:24:50.900
Our sampling was designed to examine some
of those nutrient sources and try to understand

00:24:50.900 --> 00:24:58.050
what's causing this phytoplankton biomass
and, I should say, high productivity as well.

00:24:58.050 --> 00:25:04.150
One thing that the oceanographers in the crowd
will already know, but I'll mention it to

00:25:04.150 --> 00:25:09.620
those people who don't, who aren't oceanographers,
this process of upwelling is a process by

00:25:09.620 --> 00:25:20.250
which deep water from the ocean is driven
to the surface where the nutrients contained

00:25:20.250 --> 00:25:25.170
therein can be used by surface dwelling organisms
like phytoplankton.

00:25:25.170 --> 00:25:31.780
The northern Gulf of Alaska, which I will
refer to, periodically, as the GoA, is a downwelling

00:25:31.780 --> 00:25:32.780
area.

00:25:32.780 --> 00:25:36.680
In other words, it's predominantly downwelling.

00:25:36.680 --> 00:25:40.090
The water from the depth is not being raised
to the surface.

00:25:40.090 --> 00:25:41.980
There's actually water from the surface going
down.

00:25:41.980 --> 00:25:49.030
This is a NOAA daily upwelling index which
is a function of wind largely.

00:25:49.030 --> 00:25:52.920
But the point here is that there's downwelling,
so we go into this process by which deep water

00:25:52.920 --> 00:25:56.750
gets raised to the surface, except on fairly
rare occasion.

00:25:56.750 --> 00:26:01.460
What's interesting is despite the fact that
this area is a downwelling area, you still

00:26:01.460 --> 00:26:07.390
get high concentrations of nutrients sufficient
to drive high productivity in this coastal

00:26:07.390 --> 00:26:08.390
area.

00:26:08.390 --> 00:26:12.850
Those processes are not that well understood
and that was part of the motivation for this

00:26:12.850 --> 00:26:15.160
work.

00:26:15.160 --> 00:26:23.210
Here are some basic oceanographic observations
from this coastal Gulf of Alaska area.

00:26:23.210 --> 00:26:28.370
This is just salinity in the top 40 meters
of water.

00:26:28.370 --> 00:26:30.750
A lot of information on this slide.

00:26:30.750 --> 00:26:34.510
This is collected using this device called
the mini bat by Rob Campbell of the Prince

00:26:34.510 --> 00:26:38.380
William Sound Science Center as part of our
coastal cruises.

00:26:38.380 --> 00:26:45.470
This thing flies through the water going up
and down to depths of up to 30 or 40 meters.

00:26:45.470 --> 00:26:57.070
It can essentially map out a 2D map of parameters
that can be measured, in this case, salinity.

00:26:57.070 --> 00:26:58.860
Salinity of zero is freshwater.

00:26:58.860 --> 00:27:03.420
Salinity of 35 is truly sea water.

00:27:03.420 --> 00:27:06.930
There's a series of time slices here.

00:27:06.930 --> 00:27:12.640
What I want to point out is that in March
the salinity is pretty boring, it's all fairly

00:27:12.640 --> 00:27:15.870
uniform at salinity of about 32 or so.

00:27:15.870 --> 00:27:17.640
That's because the water comes well mixed.

00:27:17.640 --> 00:27:21.860
You've got deep winter storms, there's not
really any significant river discharge at

00:27:21.860 --> 00:27:23.510
that time of year.

00:27:23.510 --> 00:27:30.670
But starting in May you begin to see this
yellow and blue region at the very surface.

00:27:30.670 --> 00:27:38.270
It's a very thin layer, only a few meters
deep and extending some tens of kilometers

00:27:38.270 --> 00:27:39.770
off shore.

00:27:39.770 --> 00:27:47.770
But that is the river plume manifesting itself
as freshwater discharge.

00:27:47.770 --> 00:27:51.450
Remember, there's not much river discharge
in the winter, hence you don't see it in the

00:27:51.450 --> 00:27:52.450
winter.

00:27:52.450 --> 00:27:55.460
But starting in May and June you start to
see this freshwater plume.

00:27:55.460 --> 00:27:59.350
That has big implications for all sorts of
things.

00:27:59.350 --> 00:28:00.350
OK.

00:28:00.350 --> 00:28:03.250
One of those things is iron.

00:28:03.250 --> 00:28:08.420
In April, which is early in the season, again,
the water column is well mixed.

00:28:08.420 --> 00:28:16.760
You get these deep storms and deep storms
lead to churning up of the bottom of sediments.

00:28:16.760 --> 00:28:21.920
That's visible in this satellite image from
up above where you can actually see this murky

00:28:21.920 --> 00:28:27.060
gray iron rich water in this whole coastal
region.

00:28:27.060 --> 00:28:32.000
This blue line represents the 500 meter contour
getting into deep water.

00:28:32.000 --> 00:28:37.640
But up until that point pretty much everything
is this murky gray and that shows up in our

00:28:37.640 --> 00:28:38.650
iron data.

00:28:38.650 --> 00:28:43.620
This is what we refer to as dissolvable iron.

00:28:43.620 --> 00:28:49.380
It's the iron that dissolves from an unfiltered
sample at pH 2.

00:28:49.380 --> 00:28:53.440
I think of it as a measure of the particle
concentration of the water.

00:28:53.440 --> 00:28:56.000
Essentially, it crosses the entire continental
shelf region.

00:28:56.000 --> 00:29:00.680
There are very high concentrations of particulate
iron and then it drops off beyond that.

00:29:00.680 --> 00:29:06.010
This continental shelf break shown with this
arrow is a real break point.

00:29:06.010 --> 00:29:11.730
It's a real point beyond which the things
really change and you see that the iron concentrations

00:29:11.730 --> 00:29:15.240
drop off dramatically beyond that.

00:29:15.240 --> 00:29:20.890
Green is a measure of the dissolved iron,
that which goes through a filter.

00:29:20.890 --> 00:29:22.470
That's more what the phytoplankton actually
use.

00:29:22.470 --> 00:29:28.540
But you see that also drops off once you get
beyond that continental shelf break.

00:29:28.540 --> 00:29:35.020
In response to all that iron, the nitrate
gets consumed.

00:29:35.020 --> 00:29:41.210
These are actual depth profiles of nitrate
from the same time frame.

00:29:41.210 --> 00:29:43.670
In green I'm showing nitrate in April.

00:29:43.670 --> 00:29:48.510
Nitrate concentrations are pretty boring in
April, they're pretty uniform, consistent

00:29:48.510 --> 00:29:51.380
with that initial slide that I showed you.

00:29:51.380 --> 00:29:56.830
The nitrate profiles are roughly 18 micromolars,
which is a high concentration.

00:29:56.830 --> 00:30:01.100
But by July that nitrate is largely gone in
the surface water.

00:30:01.100 --> 00:30:09.490
So high nitrate in spring, by the summertime
that nitrate is gone, that's because there's

00:30:09.490 --> 00:30:16.140
abundant iron and the iron is sufficient to
allow complete draw down of this nitrate.

00:30:16.140 --> 00:30:20.970
Now, I want to draw your attention to a couple
things, which I'm going to help make sense

00:30:20.970 --> 00:30:22.550
of something in a minute.

00:30:22.550 --> 00:30:27.300
Note that the nitrate concentration is depleted
in the surface waters in these more offshore

00:30:27.300 --> 00:30:33.580
stations, but there are still plenty of nitrates
below a depth of a few tens of meters in this

00:30:33.580 --> 00:30:34.630
July timeframe.

00:30:34.630 --> 00:30:39.000
That's going to help make some sense of something
in a minute.

00:30:39.000 --> 00:30:46.300
Here is a plot of chlorophyll as a function
of both time and distance.

00:30:46.300 --> 00:30:54.700
This is distance from the coast, from 0 to
25 kilometers, over time, from March through

00:30:54.700 --> 00:30:56.160
August.

00:30:56.160 --> 00:31:01.460
The thing to remember is that blue is low
chlorophyll.

00:31:01.460 --> 00:31:02.880
Red is high chlorophyll.

00:31:02.880 --> 00:31:06.520
Chlorophyll is an indication of phytoplankton
concentration, again, phytoplankton being

00:31:06.520 --> 00:31:09.250
the base of the marine food chain.

00:31:09.250 --> 00:31:14.460
In blue, early in the season in March, it's
quite boring.

00:31:14.460 --> 00:31:15.460
There's essentially no chlorophyll.

00:31:15.460 --> 00:31:17.270
There's no fresh water discharge.

00:31:17.270 --> 00:31:21.060
There's very little light, at least not enough
light to initiate a bloom.

00:31:21.060 --> 00:31:28.900
Starting in May, remember we got that river
discharge, you get riverine input that is

00:31:28.900 --> 00:31:39.360
causing a freshwater lens at the surface in
response to the freshwater input as well as

00:31:39.360 --> 00:31:42.030
the increased light levels at that time of
year.

00:31:42.030 --> 00:31:45.650
You see this chlorophyll layer, this high
chlorophyll layer.

00:31:45.650 --> 00:31:51.980
In other words, the phytoplankton are responding
to the nutrients and the light in the surface

00:31:51.980 --> 00:31:53.810
water.

00:31:53.810 --> 00:32:01.720
By May 28th, note that the phytoplankton are
largely...The concentrations are much lower

00:32:01.720 --> 00:32:06.000
in this nearshore region on May 28th.

00:32:06.000 --> 00:32:12.840
But, by the middle of May, the phytoplankton
in this midshore region, at a distance about

00:32:12.840 --> 00:32:18.830
10 to 20 kilometers or so, they've moved deeper
in the water column.

00:32:18.830 --> 00:32:20.180
They're about 20 meters.

00:32:20.180 --> 00:32:26.890
Remember, the nitrate was largely consumed
by this time, so what the phytoplankton are

00:32:26.890 --> 00:32:31.830
doing, they're actually moving down in the
water column in response to the presence of

00:32:31.830 --> 00:32:35.890
the essential nutrient, nitrate, down there.

00:32:35.890 --> 00:32:43.600
By June, July, August, the phytoplankton concentrations
across this whole transect are noticeably

00:32:43.600 --> 00:32:44.880
lower.

00:32:44.880 --> 00:32:51.500
Again, these are data by Rob Campbell from
the Prince William Sound Science Center and

00:32:51.500 --> 00:32:55.980
collected as part of our joint cruises in
this region.

00:32:55.980 --> 00:33:01.850
I want to acknowledge as well the extensive
work by Laurel McFadden, who was a Master's

00:33:01.850 --> 00:33:05.340
student of Rob Campbell at the University
of Alaska, Anchorage.

00:33:05.340 --> 00:33:10.440
She did some extensive work on the distribution
and ecology of zooplankton and juvenile pelagic

00:33:10.440 --> 00:33:13.080
fishes in the Copper River plume.

00:33:13.080 --> 00:33:20.340
I don't have time to give this work justice,
so I'm just going to acknowledge her extensive

00:33:20.340 --> 00:33:24.820
work and move on from there.

00:33:24.820 --> 00:33:31.310
I'm going to jump back very quickly to iron.

00:33:31.310 --> 00:33:37.360
Now remember, the freshwater discharge maxes
out in July and August in the Copper River.

00:33:37.360 --> 00:33:45.260
This is this transect from shore, from the
mouth of the Copper River offshore again.

00:33:45.260 --> 00:33:48.510
What you see is this low salinity water.

00:33:48.510 --> 00:33:54.960
I'm plotting both iron and salinity on the
same plot as a function of distance from shore

00:33:54.960 --> 00:33:56.210
in July.

00:33:56.210 --> 00:34:02.070
You see this low salinity water with extremely
high concentrations of iron.

00:34:02.070 --> 00:34:10.020
That's this particulate iron coming in from
this massive river discharge that's happening.

00:34:10.020 --> 00:34:18.190
In fact, if you look closely at this plot,
you see that iron and salinity, they covary

00:34:18.190 --> 00:34:19.540
at this time of year.

00:34:19.540 --> 00:34:22.669
Whenever the salinity is low, the iron is
high.

00:34:22.669 --> 00:34:25.879
Whenever the salinity is high, the iron is
low.

00:34:25.879 --> 00:34:31.619
What that's telling us is that the iron at
this time of year is coming from this glacial

00:34:31.619 --> 00:34:37.069
melt water, and it's a pretty dramatic effect.

00:34:37.069 --> 00:34:44.139
Just a quick mention of interesting phenomena
of nitrate.

00:34:44.139 --> 00:34:49.000
Remember nitrate is the limiting nutrient
for phytoplankton in much of this transect.

00:34:49.000 --> 00:34:56.500
At this low salinity time of year when the
river discharge is at its maximum, we see

00:34:56.500 --> 00:35:03.260
these low salinity surface waters and these
nearshore stations offshore the Copper River.

00:35:03.260 --> 00:35:08.210
We also see a slight enrichment in nitrate
in those surface waters.

00:35:08.210 --> 00:35:14.859
Remember this is a time of year when, by and
large, the oceanderived nitrate is consumed,

00:35:14.859 --> 00:35:20.960
but what we see is that there's nitrate enrichment
in this river plume water.

00:35:20.960 --> 00:35:26.450
It's suggestive, although not entirely convincing,
that the river is becoming a source of nitrate

00:35:26.450 --> 00:35:27.920
at that time of year.

00:35:27.920 --> 00:35:31.640
There are a couple of possible explanations
for that.

00:35:31.640 --> 00:35:37.009
One of which is that there could be nitrogenfixing
plants that are invading the landscape that

00:35:37.009 --> 00:35:39.710
are causing this nitrate delivery.

00:35:39.710 --> 00:35:44.079
There are some other possibilities as well.

00:35:44.079 --> 00:35:49.220
Very briefly, I'm going to quickly mention
another mechanism by which iron gets into

00:35:49.220 --> 00:35:52.380
the Gulf of Alaska and gets transported a
long distance.

00:35:52.380 --> 00:35:56.440
Again, this is the Copper River region.

00:35:56.440 --> 00:36:01.210
What we're looking at in this instance is
a satellite image of dust.

00:36:01.210 --> 00:36:08.410
This gray plume that you see...Here's the
scale for reference, 0 to 100 kilometers or

00:36:08.410 --> 00:36:09.410
so.

00:36:09.410 --> 00:36:15.119
This gray plume is actually atmospherically
transported dust that originates in the Copper

00:36:15.119 --> 00:36:19.529
River but also at some other sites along the
coastline.

00:36:19.529 --> 00:36:27.359
This image was created using the MODIS sensor
on satellites.

00:36:27.359 --> 00:36:35.130
It's a snapshot in time from November 6, 2006.

00:36:35.130 --> 00:36:41.000
I just want to highlight the location of Middleton
Island because, in response to this observation

00:36:41.000 --> 00:36:46.349
that there are these dust events blowing iron
and glacierderived dust out into the ocean,

00:36:46.349 --> 00:36:51.559
we set up a measurement station out on Middleton
Island.

00:36:51.559 --> 00:36:53.010
Why dust in the autumn?

00:36:53.010 --> 00:36:55.240
The river levels are low, as I mentioned earlier.

00:36:55.240 --> 00:36:57.450
There's little or no snow.

00:36:57.450 --> 00:37:02.710
There are these abundant exposed sediments.

00:37:02.710 --> 00:37:09.549
They're essentially leftover glacial flour
from the weathering that the glacier has achieved

00:37:09.549 --> 00:37:10.549
all summer long.

00:37:10.549 --> 00:37:12.780
This is fine sediment just sitting there.

00:37:12.780 --> 00:37:19.720
What happens is you get strong winds blowing
out of these mountains that resuspend a lot

00:37:19.720 --> 00:37:25.359
of this material and transport it far offshore.

00:37:25.359 --> 00:37:27.069
I alluded to Middleton Island.

00:37:27.069 --> 00:37:29.880
Here's a satellite image from November 2011.

00:37:29.880 --> 00:37:35.410
It's not nearly as dramatic an event as the
other event I showed you.

00:37:35.410 --> 00:37:42.160
Nonetheless, we have aerosol measurements
from this time interval, and, in fact, you

00:37:42.160 --> 00:37:50.279
see dust being transported and being captured
by our sampling system out on Middleton Island

00:37:50.279 --> 00:37:54.339
at exactly the same time that you see this
dust in the air.

00:37:54.339 --> 00:37:59.450
This actually was a fairly modest event by
the scale of other events that we've seen

00:37:59.450 --> 00:38:00.450
in the past.

00:38:00.450 --> 00:38:04.970
This past year, the fall of 2012, we had a
much more dramatic event.

00:38:04.970 --> 00:38:09.900
I don't have the chemistry data to share with
you, but we have the samples, and there's

00:38:09.900 --> 00:38:11.950
a lot of dust on those samples.

00:38:11.950 --> 00:38:14.569
This is just showing you the sampling equipment.

00:38:14.569 --> 00:38:16.799
Here's an aerial view of Middleton Island.

00:38:16.799 --> 00:38:19.740
This is our aerosol sampler system.

00:38:19.740 --> 00:38:25.460
I'm going to move forward just because I want
to get to the end here.

00:38:25.460 --> 00:38:29.380
That's a very, very, very quick overview of
some of the sampling.

00:38:29.380 --> 00:38:37.940
Now I want to give you a sense of some of
the modeling that's been done by a group based

00:38:37.940 --> 00:38:41.660
at the University of Maine.

00:38:41.660 --> 00:38:48.019
I'm going to show you work for which Yuan
Wang is the first author.

00:38:48.019 --> 00:38:54.490
He was a graduate student of Fei Chai and
Huijie Xue at the University of Maine, and

00:38:54.490 --> 00:39:07.049
they took an existing Gulf of Alaska physical
model and added Copper River discharge to

00:39:07.049 --> 00:39:08.049
that model.

00:39:08.049 --> 00:39:10.640
What I'm going to show you is the results
of that work.

00:39:10.640 --> 00:39:12.660
Again, here's Alaska.

00:39:12.660 --> 00:39:15.480
Here's the Copper River watershed.

00:39:15.480 --> 00:39:18.210
Here's a brief model description.

00:39:18.210 --> 00:39:22.950
This is what's referred to as a ROMS model.

00:39:22.950 --> 00:39:26.510
ROMS is short for Regional Ocean Modeling
System.

00:39:26.510 --> 00:39:33.080
It's what's referred to as a threelevel nested
model.

00:39:33.080 --> 00:39:41.970
In other words, there are different regions
of the ocean that get sampled at higher and

00:39:41.970 --> 00:39:43.790
higher resolution within the model.

00:39:43.790 --> 00:39:50.619
There's this coarser resolution region up
here, smaller region at finer resolution,

00:39:50.619 --> 00:39:59.380
and finest resolution at this Copper River
mouth region.

00:39:59.380 --> 00:40:04.079
There's horizontal resolution of 3.6 kilometers
and 40 vertical layers.

00:40:04.079 --> 00:40:08.779
I'm going to show you results from 2010 and
2011, our sampling period.

00:40:08.779 --> 00:40:16.359
Essentially what these guys have done is created
a modeling tool that can be used to simulate

00:40:16.359 --> 00:40:22.799
the entire Gulf of Alaska and, in particular,
simulate how it's influenced by discharge

00:40:22.799 --> 00:40:23.809
from the Copper River.

00:40:23.809 --> 00:40:32.880
They used realistic model forcing, including
North American Mesoscale Model meteorology.

00:40:32.880 --> 00:40:40.269
They use river discharge from the USGS office
in Anchorage, including realtime freshwater

00:40:40.269 --> 00:40:45.869
observations and nutrient concentrations,
specifically nitrate concentrations based

00:40:45.869 --> 00:40:47.980
on the river sampling that we did.

00:40:47.980 --> 00:40:50.509
They used three model cases.

00:40:50.509 --> 00:40:52.809
I'm going to show you two of those.

00:40:52.809 --> 00:40:59.130
I'm going to show you their model results
with typical river discharge and also double

00:40:59.130 --> 00:41:00.369
discharge.

00:41:00.369 --> 00:41:09.140
The double discharge is an example of what
would happen in an extreme case of warming

00:41:09.140 --> 00:41:12.730
where the discharge coming out of the Copper
River is greatly increased.

00:41:12.730 --> 00:41:22.930
That is a substantial increase, but they did
that largely to demonstrate what such a substantial

00:41:22.930 --> 00:41:24.520
increase would cause.

00:41:24.520 --> 00:41:28.930
When you use smaller perturbations, the changes
are not quite so obvious.

00:41:28.930 --> 00:41:33.579
I should say right up front, this is definitely
their work.

00:41:33.579 --> 00:41:41.369
I am not a modeler, and so I'm doing my best
to describe what I can of their model.

00:41:41.369 --> 00:41:49.460
I might have had them present this, but the
two lead scientists from this modeling effort

00:41:49.460 --> 00:41:54.190
are both in China right now, so we made a
decision that I would present it for them,

00:41:54.190 --> 00:41:55.190
and I'll do my best.

00:41:55.190 --> 00:41:57.990
This is the model topography.

00:41:57.990 --> 00:42:01.519
Again, this is the Copper River.

00:42:01.519 --> 00:42:09.869
What you see, this blocky land, that is what
really gets simulated in the model.

00:42:09.869 --> 00:42:10.869
This is Prince William Sound.

00:42:10.869 --> 00:42:12.460
This is the Copper River.

00:42:12.460 --> 00:42:15.730
These are our sampling stations over here,
just off the Copper River.

00:42:15.730 --> 00:42:21.210
I'm going to show you also data from this
mooring in the coastal region off Seward,

00:42:21.210 --> 00:42:22.779
this GAK1 location.

00:42:22.779 --> 00:42:32.119
GAK, is short for Gulf of Alaska, 1, just
to orient you here.

00:42:32.119 --> 00:42:36.630
For those of you who are not oceanographers,
it's well known and has been known for quite

00:42:36.630 --> 00:42:43.050
a long time there's a pattern of circulation
that's well documented for the Gulf of Alaska.

00:42:43.050 --> 00:42:48.701
You have these coastal currents that come
along the coastline from the south, and they

00:42:48.701 --> 00:42:53.930
bend along this northern Gulf of Alaska area
to the west, and then they turn back south

00:42:53.930 --> 00:42:55.309
again.

00:42:55.309 --> 00:42:56.920
That's well known.

00:42:56.920 --> 00:43:00.190
You're going to see that show up in the model
simulation in just a minute.

00:43:00.190 --> 00:43:04.890
Right now, I'm walking you through some still
slides, and I'm going to do a model simulation

00:43:04.890 --> 00:43:09.499
at the very end just in case there are any
hangups, so we won't be delayed by that hangup

00:43:09.499 --> 00:43:10.519
in the model.

00:43:10.519 --> 00:43:18.330
These are comparisons of the model results
with this GAK1 mooring, this coastal site.

00:43:18.330 --> 00:43:25.640
The blue data are actual observations, actual
measurements of salinity at 20 meters.

00:43:25.640 --> 00:43:27.749
The red is a model.

00:43:27.749 --> 00:43:29.059
It's not a perfect match.

00:43:29.059 --> 00:43:37.700
You'll see that in the winter, typically the
model salinity is a little bit low, and the

00:43:37.700 --> 00:43:40.940
timing of these changes is not spot on.

00:43:40.940 --> 00:43:47.930
But in general, it captures the overall flavor
of this variability in salinity in response

00:43:47.930 --> 00:43:50.720
to oceanographic processes.

00:43:50.720 --> 00:43:53.960
The model does a pretty good job although
obviously not perfect.

00:43:53.960 --> 00:43:58.799
This is a simulation of temperature.

00:43:58.799 --> 00:44:08.549
The model does a pretty good job of simulating
temperature.

00:44:08.549 --> 00:44:15.359
Temperatures are a little bit cooler in the
model much of the time, but they're pretty

00:44:15.359 --> 00:44:16.359
close.

00:44:16.359 --> 00:44:24.160
What I'm going to show you is the results
of a tracer experiment where they initiated

00:44:24.160 --> 00:44:26.759
this modelonly tracer.

00:44:26.759 --> 00:44:30.740
There's essentially discharge happening from
the Copper River and coming out of the Copper

00:44:30.740 --> 00:44:31.740
River.

00:44:31.740 --> 00:44:36.030
This is just to show where this water from
the Copper River goes and what happens to

00:44:36.030 --> 00:44:38.829
it and what the impacts are of some of that
water.

00:44:38.829 --> 00:44:41.150
This is not really salinity.

00:44:41.150 --> 00:44:45.539
You can think of it as freshwater, but it's
not really.

00:44:45.539 --> 00:44:48.930
It's something that you can do in a model
that's a lot harder to do in the real world.

00:44:48.930 --> 00:44:54.950
They essentially created this fake parameter
that they could trace, essentially just to

00:44:54.950 --> 00:44:57.829
show where the Copper River discharge goes.

00:44:57.829 --> 00:45:02.470
That was the whole point of it.

00:45:02.470 --> 00:45:09.250
Just to give some background, this two times
discharge is not completely arbitrary.

00:45:09.250 --> 00:45:11.269
It's quite a big perturbation.

00:45:11.269 --> 00:45:19.290
Ed Josberger's work from the Bering Glacier
suggests that if we had substantial warming

00:45:19.290 --> 00:45:28.650
to the tune of about four or five degrees,
you would get double the melt discharge, double

00:45:28.650 --> 00:45:35.829
the summer discharge from the Bering Glacier,
just to give you a rough idea.

00:45:35.829 --> 00:45:39.799
Again, I'm going to show you still shots,
which are not as instructive as the video,

00:45:39.799 --> 00:45:45.710
but I'm going to do it just because there's
potential that the video's going to have problems.

00:45:45.710 --> 00:45:54.250
In a nutshell, these are simulations from
July 10th, from both 2010 and 2011.

00:45:54.250 --> 00:46:00.130
This upper left panel is just the normal discharge
with the normal river discharge.

00:46:00.130 --> 00:46:04.519
You see this Copper River plume extending
out into the ocean.

00:46:04.519 --> 00:46:11.339
With two times the river discharge, you see
a much larger area impacted by that Copper

00:46:11.339 --> 00:46:12.450
River plume.

00:46:12.450 --> 00:46:18.430
2011, it's a little bit different because
the conditions were a little bit different,

00:46:18.430 --> 00:46:21.250
but the contrast is the same pretty much.

00:46:21.250 --> 00:46:30.789
The region affected by this discharge being
doubled is quite a bit larger than in the

00:46:30.789 --> 00:46:32.900
normal river discharge example.

00:46:32.900 --> 00:46:40.450
Just to give a sense of where this water's
going in terms of a mass balance, if you have

00:46:40.450 --> 00:46:48.650
a hundred units of water coming out of the
Copper River, a lot of it is going to be transported,

00:46:48.650 --> 00:46:51.829
as I mentioned before, to the west.

00:46:51.829 --> 00:46:54.840
Some of it's going to go into Prince William
Sound.

00:46:54.840 --> 00:46:56.749
Some of it's going to come back out of Prince
William Sound.

00:46:56.749 --> 00:47:04.270
Almost none of it is going to travel to the
east because the prevailing currents are towards

00:47:04.270 --> 00:47:06.339
the west.

00:47:06.339 --> 00:47:10.940
What I want to draw your attention to at the
moment is this contrast in what is transported

00:47:10.940 --> 00:47:13.650
offshore.

00:47:13.650 --> 00:47:17.339
The red line is the normal river discharge
transport.

00:47:17.339 --> 00:47:23.430
It's only 3.8 percent of the total, but contrast
that with the two times river discharge.

00:47:23.430 --> 00:47:29.609
If you double the river discharge, you have
a 300 percent increase in offshore transport.

00:47:29.609 --> 00:47:38.920
In other words, it's three times as much transport
offshore of this riverinfluenced water.

00:47:38.920 --> 00:47:47.369
That's one important difference of this double
discharge scenario on the physical circulation.

00:47:47.369 --> 00:47:55.800
As a part outreach and part science effort,
Rob Campbell conducted an experiment in collaboration

00:47:55.800 --> 00:47:57.779
with the native village of Eyak.

00:47:57.779 --> 00:48:00.930
This is a native group in Cordova, Alaska.

00:48:00.930 --> 00:48:02.910
Again, this is Prince William Sound.

00:48:02.910 --> 00:48:04.490
This is the Copper River.

00:48:04.490 --> 00:48:06.140
They released these drifters.

00:48:06.140 --> 00:48:10.220
These are devices that essentially float with
the water.

00:48:10.220 --> 00:48:16.119
They did it three times in 2011, in March,
May, and July.

00:48:16.119 --> 00:48:21.960
These devices have GPS on them, so they can
be tracked and see where they go over time

00:48:21.960 --> 00:48:23.480
and see where they end up.

00:48:23.480 --> 00:48:31.430
What you see is, at all times, these drifters
were transported along the coast and to the

00:48:31.430 --> 00:48:38.549
west as the theory would predict and as the
model would predict.

00:48:38.549 --> 00:48:40.410
Some of them went into Prince William Sound.

00:48:40.410 --> 00:48:42.579
Some of them came back out.

00:48:42.579 --> 00:48:49.430
The drifter experiment, while limited in scope
with only three drifters, essentially confirms

00:48:49.430 --> 00:48:51.980
the predictions of the model.

00:48:51.980 --> 00:48:53.980
It's a nice validation.

00:48:53.980 --> 00:48:59.609
I mentioned it's part outreach, part science
experiment, but it's a neat confirmation of

00:48:59.609 --> 00:49:03.509
what we think we know about circulation in
the area.

00:49:03.509 --> 00:49:07.329
I'm just going to conclude, and then I'm going
to come back and show that video.

00:49:07.329 --> 00:49:12.849
Just to conclude, I hope I convinced you that
glaciers are losing mass in the Gulf of Alaska

00:49:12.849 --> 00:49:16.509
region, as in other regions worldwide.

00:49:16.509 --> 00:49:20.650
Glacier melt is a source of iron to the coastal
Gulf of Alaska region.

00:49:20.650 --> 00:49:28.460
There's summertime river discharge, when much
of the fine particulate mass in that river

00:49:28.460 --> 00:49:32.289
actually gets out of the ocean and escapes
the estuary.

00:49:32.289 --> 00:49:36.619
Hence that glacierdriven discharge is important.

00:49:36.619 --> 00:49:42.030
In the wintertime, there's sediment resuspension
from the continental shelf region.

00:49:42.030 --> 00:49:44.849
That still is this fine particulate matter
from the glacier.

00:49:44.849 --> 00:49:49.670
It's just that it's settled out into the sediments,
but it gets resuspended every year in the

00:49:49.670 --> 00:49:51.309
winter.

00:49:51.309 --> 00:49:57.239
In the autumn, there's dust derived from these
winds that race down those mountain valleys

00:49:57.239 --> 00:50:02.529
and transport this fine sediment out from
these river valleys hundreds of kilometers

00:50:02.529 --> 00:50:04.010
out into the ocean.

00:50:04.010 --> 00:50:10.950
I want to paint a picture of very seasonally
variable sources of iron to this coastal Gulf

00:50:10.950 --> 00:50:14.130
of Alaska region.

00:50:14.130 --> 00:50:19.450
In the winter, there's deep, deep mixing as
you get strong storms and limited river discharge.

00:50:19.450 --> 00:50:25.339
That leads to the water column being very
well mixed and churned up and leads to high

00:50:25.339 --> 00:50:31.239
concentrations of iron and nitrate in surface
waters, which together fuel high spring phytoplankton

00:50:31.239 --> 00:50:34.040
biomass on the shelf.

00:50:34.040 --> 00:50:37.650
Nitrate is actually the limiting nutrient
on our shelf transect.

00:50:37.650 --> 00:50:45.059
I didn't actually show you, but Laurel's work
suggests that zooplankton and fish she sampled

00:50:45.059 --> 00:50:49.359
tend to be more abundant within the river
plume than outside the river plume.

00:50:49.359 --> 00:50:59.069
That's in response to evasion of predators
in these turbid river waters.

00:50:59.069 --> 00:51:04.329
I want to emphasize that melting of glaciers
is perturbing these nutrient cycles in ways

00:51:04.329 --> 00:51:09.550
that we do not fully understand, although
there is a suggestion that the rivers are

00:51:09.550 --> 00:51:12.770
now becoming a summertime source of nitrate.

00:51:12.770 --> 00:51:19.059
In the winter, the ocean is that source of
nitrate, but that nitrate gets used up by

00:51:19.059 --> 00:51:24.569
massive phytoplankton blooms in the spring
and by the summertime, these glacierdominated

00:51:24.569 --> 00:51:32.130
rivers are becoming a source of nitrate, with
a few different possibilities for sources.

00:51:32.130 --> 00:51:36.799
Impacts of the increased river discharge in
response to the increased melt include...There's

00:51:36.799 --> 00:51:41.660
a larger area of Copper River plume.

00:51:41.660 --> 00:51:46.059
There's increased offshore transport of this
river water, which includes particulate iron

00:51:46.059 --> 00:51:51.089
and other species as well.

00:51:51.089 --> 00:51:53.869
There's most likely increased stratification.

00:51:53.869 --> 00:51:58.569
In other words, that freshwater layer is less
dense.

00:51:58.569 --> 00:52:03.890
It resides in its surface, and it reduces
vertical mixing.

00:52:03.890 --> 00:52:08.989
The deep water can't mix up to the surface,
and that probably translates to reduced nitrate

00:52:08.989 --> 00:52:10.880
flux to the surface.

00:52:10.880 --> 00:52:19.420
Some ecosystem responses in response to such
a perturbation of increased Copper River discharge...These

00:52:19.420 --> 00:52:24.650
are fairly speculative, and I have to take
ownership for this part.

00:52:24.650 --> 00:52:28.650
This is my speculation.

00:52:28.650 --> 00:52:33.880
These ecosystem responses might include increased
productivity beyond the shelf in response

00:52:33.880 --> 00:52:39.750
to that increased offshore transport of iron
and reduced productivity over the shelf in

00:52:39.750 --> 00:52:44.010
response to that increased stratification
that limits nitrate flux to the surface.

00:52:44.010 --> 00:52:54.079
I just want to mention that impacts on eddies
are beyond the scope of this project.

00:52:54.079 --> 00:52:56.490
I'm going to try to show a video quickly.

00:52:56.490 --> 00:52:59.289
Should I make this full screen?

00:52:59.289 --> 00:53:00.289
Ashley: �Yes.

00:53:00.289 --> 00:53:03.369
John: �What I'm going to show you is a video.

00:53:03.369 --> 00:53:07.890
This is a simulation of that discharge from
the Copper River to give you a sense of the

00:53:07.890 --> 00:53:08.890
power of this.

00:53:08.890 --> 00:53:10.560
This is actually a really nice tool.

00:53:10.560 --> 00:53:18.829
Again, the people from the Gulf of Maine added
the Copper River discharge to this Gulf of

00:53:18.829 --> 00:53:23.849
Alaska model, and with that, we can now understand
impacts of Copper River discharge on this

00:53:23.849 --> 00:53:26.470
entire northern Gulf of Alaska region.

00:53:26.470 --> 00:53:33.180
Just to orient you, this is discharge from
the Copper River, a tracer, if you will.

00:53:33.180 --> 00:53:36.660
It's just Copper River water, not really salinity.

00:53:36.660 --> 00:53:39.440
I want to point out the date at the top.

00:53:39.440 --> 00:53:40.589
It's May 1st, 2010.

00:53:40.589 --> 00:53:47.059
You'll see the date click along, and you'll
see this river water discharge come out through

00:53:47.059 --> 00:53:49.359
this Copper River mouth in just a second.

00:53:49.359 --> 00:53:51.019
Bear with me.

00:53:51.019 --> 00:53:55.519
Now you see the dates moving along.

00:53:55.519 --> 00:54:03.289
You see increased discharge in response to
increased melt in the summer and this phenomenon

00:54:03.289 --> 00:54:06.769
of this water being transported along shore.

00:54:06.769 --> 00:54:10.450
Now it's July.

00:54:10.450 --> 00:54:16.759
We're getting close to the period of peak
discharge, and you'll begin to see this Copper

00:54:16.759 --> 00:54:19.220
River water going into Prince William Sound.

00:54:19.220 --> 00:54:21.130
There you go.

00:54:21.130 --> 00:54:25.269
Some of it makes its way into Prince William
Sound, and it's harder to see it coming out

00:54:25.269 --> 00:54:26.769
again.

00:54:26.769 --> 00:54:33.480
Now the discharge is diminishing as summer
winds down.

00:54:33.480 --> 00:54:43.150
It just gives you a feeling for the power
of this modeling approach.

00:54:43.150 --> 00:54:46.089
Now we're into the autumn when there's much
less discharge.

00:54:46.089 --> 00:54:50.569
I think I can stop it there.

00:54:50.569 --> 00:54:53.930
I'd be happy to take any questions.

00:54:53.930 --> 00:54:54.930
Phew.

00:54:54.930 --> 00:54:55.930
Got through it.

00:54:55.930 --> 00:54:57.769
Ashley: �[laughs] Thanks John.

00:54:57.769 --> 00:55:07.162
If you guys would like to ask a question...We
do have one question from Gwenn, and it says,

00:55:07.162 --> 00:55:13.150
"How bioavailable is the particulate iron
from the glacier melt waters"?

00:55:13.150 --> 00:55:15.920
John: �That's a good question.

00:55:15.920 --> 00:55:22.950
I perhaps should have gone into that, but
I had to gloss over a lot of details.

00:55:22.950 --> 00:55:25.319
It's a very good question.

00:55:25.319 --> 00:55:34.400
Most of that is not bioavailable, but the
thing to keep in mind is that it's a massive,

00:55:34.400 --> 00:55:35.400
massive quantity.

00:55:35.400 --> 00:55:43.329
It just takes a small amount of dissolution
of that massive quantity of particulate iron

00:55:43.329 --> 00:55:53.210
to translate to a lot of iron in parts of
the dissolved phase.

00:55:53.210 --> 00:56:01.029
This is a complicated thing to quantify, and
there are various ways of doing it.

00:56:01.029 --> 00:56:09.829
Numbers that people throw out there as ballpark
estimates of how much of that is available

00:56:09.829 --> 00:56:15.660
would be something in the range of maybe 2
to 20 percent.

00:56:15.660 --> 00:56:21.279
The literature on this is pretty confusing
because there are estimates that range from

00:56:21.279 --> 00:56:26.400
well under 2 to well over 20 percent.

00:56:26.400 --> 00:56:31.569
In a nutshell, if you have a small amount
of particulate matter in a large amount of

00:56:31.569 --> 00:56:37.950
water, you tend to dissolve a higher proportion
of that particulate matter.

00:56:37.950 --> 00:56:40.720
Anyway, that's a quick answer to that.

00:56:40.720 --> 00:56:43.369
Does that answer your question?

00:56:43.369 --> 00:56:48.089
Ashley: �Gwenn says, "Yes, thank you."

00:56:48.089 --> 00:56:49.660
John: �OK.

00:56:49.660 --> 00:56:56.809
Ashley: �I know that we're running a little
bit late, but if there are any last minute

00:56:56.809 --> 00:57:01.140
questions...We do have one from Benjamin,
and it says, "At the beginning of your presentation,

00:57:01.140 --> 00:57:07.810
I think that you said that the GoA was not
a nitrogenlimited system but, on the conclusion

00:57:07.810 --> 00:57:15.020
slide, that you said there was a transect
that was nitrogenlimited.

00:57:15.020 --> 00:57:22.460
Did I see that right, and, if so, why the
difference?"

00:57:22.460 --> 00:57:27.109
John: �Perhaps I glossed over that too quickly.

00:57:27.109 --> 00:57:33.869
The broader Gulf of Alaska is ironlimited,
but the coastal region tends to be nitratelimited.

00:57:33.869 --> 00:57:40.539
It depends on the time of year and where exactly
you're talking about.

00:57:40.539 --> 00:57:48.630
Early in the growing season, it's not limited
at all because there's abundant nitrate and

00:57:48.630 --> 00:57:52.569
abundant iron.

00:57:52.569 --> 00:57:55.390
One or the other tends to the limiting nutrient.

00:57:55.390 --> 00:58:04.470
By the time midsummer rolls along, in the
coastal region, what I tried to emphasize

00:58:04.470 --> 00:58:10.979
is that nitrate tends to be fully consumed,
and so nitrate tends to be limiting in that

00:58:10.979 --> 00:58:12.410
coastal area.

00:58:12.410 --> 00:58:14.869
Iron is more limiting farther offshore.

00:58:14.869 --> 00:58:18.570
That's not always the case.

00:58:18.570 --> 00:58:23.509
There are some coastal areas where they're
ironlimited, but, at least from our data,

00:58:23.509 --> 00:58:31.050
it would appear that nitrate is actually the
limiting nutrient in the summer, in the nearshore

00:58:31.050 --> 00:58:32.170
region.

00:58:32.170 --> 00:58:36.450
Somewhere out beyond the continental shelf
break is where iron limitation kicks in.

00:58:36.450 --> 00:58:39.400
Ashley: �Thank you.

00:58:39.400 --> 00:58:45.569
We have a question from Tom, and it says,
"What is the relationship between the Copper

00:58:45.569 --> 00:58:50.549
River outflow nutrients and the downwellingupwelling
nutrient input"?

00:58:50.549 --> 00:58:53.000
John: �Good question.

00:58:53.000 --> 00:58:55.460
Again, something I really glossed over.

00:58:55.460 --> 00:59:04.690
I have to preface this by saying that the
people who could best answer that question

00:59:04.690 --> 00:59:11.550
would be the modelers, and that's not me.

00:59:11.550 --> 00:59:22.010
The Copper River discharge into the ocean
induces a process by which, at least it can

00:59:22.010 --> 00:59:30.490
induce a process by which you get upward mixing
of nutrients from below in an estuarine circulation

00:59:30.490 --> 00:59:37.500
where you get outflow at the surface of this
freshwater, and that induces entrainment of

00:59:37.500 --> 00:59:43.920
water below that that causes a return flow
and an upwelling.

00:59:43.920 --> 00:59:52.089
The presence of the river itself can induce
this upward, sort of an upwelling in the vicinity

00:59:52.089 --> 00:59:53.549
of the river plume.

00:59:53.549 --> 00:59:58.180
That's one reason that river plumes can be
fairly productive, because you have all this

00:59:58.180 --> 01:00:01.880
mixing going on of deeper water being raised
to the surface.

01:00:01.880 --> 01:00:07.710
That's a process that's somewhat independent
of this downwellingupwelling phenomenon.

01:00:07.710 --> 01:00:19.180
The upwelling index that I showed, which tended
to show primarily downwelling, that's more

01:00:19.180 --> 01:00:25.569
relevant to regions outside of the influence
of the river, where the prevailing winds are

01:00:25.569 --> 01:00:29.920
largely what drive that.

01:00:29.920 --> 01:00:39.400
The winds are such that you tend to get downwelling,
except in fairly rare occasions, in that part

01:00:39.400 --> 01:00:40.400
of the world.

01:00:40.400 --> 01:00:43.869
I'm not sure if I answered your question,
but that's one attempt.

01:00:43.869 --> 01:00:56.619
Ashley: �Tom, if you just want to chat "yes"
or "no," that would be great.

01:00:56.619 --> 01:01:00.869
He said, "Yes, it does.

01:01:00.869 --> 01:01:02.570
Thank you."

01:01:02.570 --> 01:01:04.270
John: �OK.

01:01:04.270 --> 01:01:10.579
Ashley: �We have one more question from
Patricia, and it says, "Have you looked at

01:01:10.579 --> 01:01:16.130
how productivity varies with PDO or other
climate variation?

01:01:16.130 --> 01:01:21.080
Put another way, do the local factors you
discussed dominate productivity shifts, or

01:01:21.080 --> 01:01:26.989
do other factors like PDO dominate productivity
at certain times or phases?"

01:01:26.989 --> 01:01:30.920
John: �Very good question.

01:01:30.920 --> 01:01:39.650
Let's see, it's hard for me to give a short
answer to that question.

01:01:39.650 --> 01:01:45.109
Different people define productivity in different
ways.

01:01:45.109 --> 01:01:52.670
Often people use the satellite image of Chlorophyll
to say something about productivity.

01:01:52.670 --> 01:01:56.799
Chlorophyll was pretty much the only thing
I showed in this presentation but that really

01:01:56.799 --> 01:02:05.859
is a measure of phytoplankton biomass whereas
productivity is a rate that isn't really measured

01:02:05.859 --> 01:02:09.690
by that Chlorophyll concentration.

01:02:09.690 --> 01:02:16.329
To get at productivity requires, well, there's
a whole bunch of different methods that people

01:02:16.329 --> 01:02:19.390
use.

01:02:19.390 --> 01:02:24.249
The classical way is to incubate samples in
a bottle, radiocarbon labeling.

01:02:24.249 --> 01:02:30.089
Paul Clay, here at the University of Washington,
is one of the people who has come up with

01:02:30.089 --> 01:02:40.640
a very elegant way, using dissolved gas measurements
to get at this rate of carbon uptake or option

01:02:40.640 --> 01:02:41.640
production.

01:02:41.640 --> 01:02:46.219
In a nutshell, you get different answers depending
on how you measure it.

01:02:46.219 --> 01:02:53.349
The bottle method I mentioned is an instantaneous
snapshot plus there is sometimes bottle effects.

01:02:53.349 --> 01:02:55.650
I'm not trying to waffle.

01:02:55.650 --> 01:03:04.219
I'm trying just to say, there really aren't
sufficient observations with enough different

01:03:04.219 --> 01:03:06.670
techniques to answer that question.

01:03:06.670 --> 01:03:18.289
Because you get variation, the different methods
disagree by many times, by two to eight times

01:03:18.289 --> 01:03:19.289
when you intercompare them.

01:03:19.289 --> 01:03:24.380
There really needs to be more intercomparison
of these various methods of inferring biological

01:03:24.380 --> 01:03:25.380
productivity.

01:03:25.380 --> 01:03:28.049
There hasn�t been a lot of that.

01:03:28.049 --> 01:03:39.660
Until there is a rigorous intercomparison,
I don't feel like I can answer that question.

01:03:39.660 --> 01:03:49.200
No doubt broad scale oceanographic processes,
such as the PDO, which by the way, stands

01:03:49.200 --> 01:03:53.660
for Pacific Decadal Oscillation, for those
who don't know that term.

01:03:53.660 --> 01:04:01.230
They are going to have a big influence on
biological processes in the broad Gulf of

01:04:01.230 --> 01:04:03.069
Alaska.

01:04:03.069 --> 01:04:09.789
Our work was focused more on the coastal region
off shore of the Copper River, which is heavily

01:04:09.789 --> 01:04:11.779
influenced by the processes in the Gulf of
Alaska.

01:04:11.779 --> 01:04:17.460
It is its own beast in a way too, because
of the tremendous amount of fresh water discharge

01:04:17.460 --> 01:04:23.559
coming out there which influences nutrients
and stratification.

01:04:23.559 --> 01:04:33.430
Ashley: �All right, I'm just scanning for
any additional questions.

01:04:33.430 --> 01:04:38.640
Patricia said, "Thank you very much."

01:04:38.640 --> 01:04:48.479
We do have another one from Kay and it says,
"How might ocean acidification affect the

01:04:48.479 --> 01:04:53.420
iron concentration in the model, if at all?

01:04:53.420 --> 01:04:54.599
(Fe)."

01:04:54.599 --> 01:05:00.499
John: �Another very good question.

01:05:00.499 --> 01:05:07.690
The first primary thing I have to say is that
I don't think we know, and not because of

01:05:07.690 --> 01:05:08.979
insufficient observations.

01:05:08.979 --> 01:05:18.259
Your first instinct is that ocean acidification
would lead to greater iron concentrations.

01:05:18.259 --> 01:05:22.269
The solubility of iron is a function of pH.

01:05:22.269 --> 01:05:27.650
Now, ocean acidification is a pretty small
perturbation of pH.

01:05:27.650 --> 01:05:33.559
But, when the ocean gets more acidic, there's
going to tend to be a little more solubility

01:05:33.559 --> 01:05:34.559
of iron.

01:05:34.559 --> 01:05:40.789
If anything, acidification, in and of itself,
is probably going to cause slight increase

01:05:40.789 --> 01:05:44.089
in iron concentration.

01:05:44.089 --> 01:05:50.420
Having said that, it's probably likely that
ocean acidification is going to have so many

01:05:50.420 --> 01:06:02.130
other impacts, that that pH effect, by itself,
is going - well and this is my own gut feeling

01:06:02.130 --> 01:06:08.400
- it's going to be dominated by other things
that are also going to effect the iron concentration.

01:06:08.400 --> 01:06:14.420
Just pH alone is going to affect the iron
solubility and iron concentration.

01:06:14.420 --> 01:06:19.299
Ashley: �Thank you John.

01:06:19.299 --> 01:06:26.619
I'm not seeing any more questions.

01:06:26.619 --> 01:06:30.269
Kay says, "Thank you very much, John."

01:06:30.269 --> 01:06:38.450
All right, I'd like to thank John for an excellent
presentation and that was very informative.

01:06:38.450 --> 01:06:38.959
Transcription by CastingWords
p.


