WEBVTT

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[SQUEAKING]

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[RUSTLING]

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[CLICKING]

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R. SCOTT KEMP: We're going
to figure out how many people

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nuclear power kills.

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I mean, we need
an answer to this.

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So this is part of the
externalities calculation.

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If you recall, we spent
the first major part

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of the class working out the
explicit internalized economics.

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But I said that that's
not the whole story.

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We need also to
have externalities.

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One externality
is climate change.

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We talked about the difficulty
of coming up with a number.

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So we said, well,
we'll take the view

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that we don't know
what it is, but we

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will be able to estimate
how big it would

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have to be to justify things.

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But the difficulty
of that is that

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under equal decarbonization,
wind and solar mostly

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outcompetes nuclear, except for
in the thermal markets where

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there's potentially
some opportunity.

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And now the question is, is
there an additional safety

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externality associated with
nuclear, or other externalities

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associated with wind or solar or
natural gas that actually change

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the ordering, if you will?

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We've done everything
from explicit perspective.

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What about these externalities?

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What if it turns out that

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"Windmills are killing the birds."
turns out to be a big problem?

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So we need to get into that.

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But the first thing
we're going to do

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is calculate the
externality for nuclear.

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So who has seen this plot?

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How many people feel they were--

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yeah.

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How many people feel
that this plot actually

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influenced their choice to
become nuclear engineers?

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Yes?

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No?

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There's a kind of a shaky head.

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One half person says this
plot had influence on them.

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It's a nice plot.

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I hope it's right.

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We'll find out.

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That's what we're
going to do today.

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We're going to figure
out what this plot is.

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So let's go.

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So I showed you this
slide Wednesday.

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This is some of
the isotopes that

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come out of reactor accidents
which have large activity.

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And we mentioned that cesium--
sorry, the European spelling--

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cesium-137 and
also cesium-134 is

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significant on the early days.

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And these other ones, they
dominate hundreds of years.

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But this is a log plot here.

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And these are the two isotopes
of principal interest--

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cesium-134 and cesium-137.

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Iodine-131, which is
not shown on this plot,

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is even more important.

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It has a very short half life.

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So it decays entirely in a
few months, a couple of years,

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basically.

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And it gives a big dose that we
also have to take into account.

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But it is a different dynamic
because it is short-lived.

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It's what you eat and
breathe immediately

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following the accident.

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This other stuff,
cesium just hangs around

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for centuries and just increases
slowly the background radiation

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dose.

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So we are going to do the
calculation for cesium.

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We'll look at some of
the other isotopes.

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We'll add in iodine, but
we won't do the calculation

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explicitly.

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And we'll just try to take into
account the biggest and most

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important isotopes and
get a measure of the dose.

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Just as a mention, you've seen
the periodic table before.

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Why is cesium-- and another one
people hear about strontium-90?

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Why is strontium and
caesium important?

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Well, because of the
valence electrons

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are similar to in a case
of strontium like calcium.

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So it sits in our bones.

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It's not a big beta-- it's
not a big external emitter.

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If you're around
strontium contamination,

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it's not a problem.

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But if you eat
it, it's a problem

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because it then gets
taken into your bones.

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And so like the
history of above ground

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nuclear weapons
testing was that we

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were testing all these
nuclear bombs, which

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are little mini
fission reactors, which

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disperse all of their fission
products into the environment.

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And we were just--
the US government

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and other governments
were doing this.

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And then it turned out that the
strontium was emplacing itself

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in the teeth of babies.

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Instead of calcium
apatite, which

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is the enamel coating of your
teeth, it was strontium apatite.

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And you could measure
the radioactivity

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of the teeth of newborn
baby-- of young babies.

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And this fact caused
essentially a political movement

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that forced nuclear weapons
testing underground.

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So, in fact, the amount of
fission products released

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from typical nuclear
weapons is actually

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a lot smaller than what we
would get from a large accident.

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So strontium does matter,
mainly for ingestion pathways.

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We're not going
to talk about it.

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Cesium looks like potassium.

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And so potassium is used
everywhere in your body.

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So it just filters through all
of your organs and stays around.

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So let's look at some
of the source terms.

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We're going to look at
two major accidents--

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the two INES 7 events.

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This is an international
nuclear event scale.

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It goes up to 7.

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7 is the worst.

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There has only been two of
these events in history--

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Chernobyl and Fukushima.

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So let's look at those
events because they

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dominate the source.

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So Chernobyl was an RBMK-type
water graphite reactor.

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It had no containment.

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They believed that it
wasn't really possible.

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A steam explosion ejected
fuel and melted the fuel

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and triggered fires.

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And the fires then helped to
volatilize a lot of the fission

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products that were in the fuel
that boil off at temperatures

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below the fire temperature.

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So there are still 11 of
these reactors operating

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in the world today, all in
the former Soviet Union.

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So they continue to pose
whatever threat they pose.

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AUDIENCE: [INAUDIBLE] as the
Soviets did actually make

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some changes after Chernobyl.

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They're not exactly the same,

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R. SCOTT KEMP: Yes, but they
still don't have containment.

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So this thing released 85
petabecquerels of cesium 137,

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4,000 petabecquerels of
non-noble gas activity total.

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But remember, petabecquerel
is just decays.

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It doesn't tell you
how bad the decays are.

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It doesn't tell you how much
energy is in those decays.

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So it's not-- you can't
just scale this number.

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The number we want
to use here is 85.

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This is the contamination
as calculated by the French.

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I think this is
IRSN across Europe.

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75% of the total
release is estimated

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to have been deposited on
land somewhere in the world.

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And this is a log scale,
so it's a little bit tricky

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to try to interpret.

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Fortunately, if we
wanted to measure

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the average contamination,
say, in all of Europe,

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we could try to voxelize or
pixelize this and figure it out.

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But this European Commission
issued this report in 1998,

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and they did it for us.

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And their number
is 7 kilobecquerels

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is the European spatial
average contamination--

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7 kilobecquerels of
cesium-137 per meter squared.

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So that's good to know.

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Now let's make a little
observation here.

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The first observation is
that in the last class

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I defended the linear
no threshold model.

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If the linear no threshold
model is correct,

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then that means 10 millisieverts
of dose to one person

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is the same as 1 millisieverts
of dose to 10 people.

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And so that makes calculating
the dose response really easy.

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We just basically need to
estimate the average population

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times the average dose.

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And because it's all linear,
it's roughly correct.

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And that's what
we're going to do.

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Now, what we really care
about is not the average land

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contamination.

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It's the average
exposure to a person.

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And people aren't evenly
spread across all of the land.

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People-- like Western Europe
has a higher population density

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than Siberia.

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And so we need to maybe
accommodate for that.

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A thing that has been raised
is that Ukraine, which I've now

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outlined here for you in
black, is sometimes called

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the bread bowl of Europe.

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A huge amount of
grain is grown there,

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which uptakes cesium
from the ground--

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looks like potassium--
into the grain.

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And then you eat it, and
you have an ingestion dose.

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So arguably, the
European spatial average,

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which includes all of uneventful
space, is probably too low.

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Since we're really in the domain
of single digits of significance

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here, I'm just
going to round this

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to 10, to take into account
the fact that they grow

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a lot of grain here, and Europe
is here, and so on and so forth.

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Yep.

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AUDIENCE: Are you
taking into account

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that that grain still has to
pass radiological standards

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for the European--

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R. SCOTT KEMP: It will.

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AUDIENCE: Say again.

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R. SCOTT KEMP: It will.

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Yeah.

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It still passes the standards.

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It's just that it's going
to be higher than it was.

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So that's what we're looking at.

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The effect is very,
very small amounts

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of dose times very
large numbers of people.

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And that's what we
have to deal with.

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Here's Fukushima.

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21 petabecquerels instead of 85.

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It's a BWR type reactor,
water moderated,

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high-pressure containment, much
more similar to the reactors

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that we have operating today.

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There are-- I have
to double-check this.

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I think there are 94 of
these reactors in the world,

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but I don't think
all of them are

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operating because a lot
of them were shut down.

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But it's higher than 11.

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The accident at
Fukushima was really

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initiated by the tsunami
that followed the earthquake.

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The reactors were OK.

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After the earthquake, one
of the reactors had been--

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they were already shut down
because of the earthquake

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for about an hour.

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But then the cooling
systems failed.

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And as a result, the fuel
got hotter, and eventually

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got hot enough to
boil away the water

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and begin to melt and
release fission products.

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Although the Fukushima reactor
did have a small containment,

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hydrogen caused explosions, and
that eventually, caused exposure

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to the spent fuel pool,
which we talked about could

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have caught on fire.

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And NRC says if it
had, the situation

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would have been 100 times
worse or 25 times worse

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than Chernobyl.

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Fortunately, that didn't happen.

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But they still had to
vent the containment,

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the high-pressure containment,
to prevent it from rupturing.

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And so that's where
the releases--

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significant releases came
from these venting events.

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So the total amount released
was still much smaller.

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And here is the situation for
the releases from Fukushima.

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So you see these momentary
pulses where they release some,

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and then they close
the containment.

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Again, they release
some more and so on.

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Let me see if I can
speed this along.

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Yeah.

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So you can see, the lucky
thing about Fukushima

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is the winds off the
Kanto plane of Japan

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almost always blow
into the Pacific Ocean.

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And so we really got lucky where
these very high-dose plumes that

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might have contaminated
a large land area,

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basically all just got
washed into the ocean.

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However, a lot did get to
the United States and Canada.

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And I'll show you-- here is the
final deposited contamination.

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And it turns out that the United
States probably got more--

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I mean, the North
America probably

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got more contamination in total
than Japan from this accident.

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The thing I want you to
take away from this chart,

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again, keeping in mind
linear no threshold,

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is that the
contamination here is

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about, let's say, 1%
of the contamination,

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the average contamination here--

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something of order, 1%.

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But the land area here is
roughly of order 100 times

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the land area that is
contaminated over here.

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So we could say, very
roughly, since we're

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doing a back of the
envelope calculation,

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that the global contamination
might be like a factor of 2,

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higher than the
local contamination.

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Something like that.

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It turns out you
don't have to rely on

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of rough hand-waving argument.

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UNSCEAR has actually
done a calculation

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I will show you later.

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And when they compared
Europe to global,

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they found a factor of 1.6.

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It depends where the oceans are.

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Depends where the
winds are blowing.

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Depends where the reactors are.

00:14:41.040 --> 00:14:42.820
All these things matter.

00:14:42.820 --> 00:14:46.360
But there's roughly, very
roughly, a factor of 2--

00:14:46.360 --> 00:14:48.320
less than a digit
of significance.

00:14:48.320 --> 00:14:51.140
So that's a good thing
to keep in your mind.

00:14:51.140 --> 00:14:57.400
So what is a, quote, "typical"
major in INES 7 reactor

00:14:57.400 --> 00:14:57.900
accident?

00:14:57.900 --> 00:14:58.720
Yeah?

00:14:58.720 --> 00:15:00.095
AUDIENCE: I have
a quick question

00:15:00.095 --> 00:15:04.120
about how much is
1 kilo becquerel

00:15:04.120 --> 00:15:07.140
per square meter compared to
just background radiation?

00:15:12.280 --> 00:15:15.040
R. SCOTT KEMP: I think
background contamination

00:15:15.040 --> 00:15:19.600
from nuclear weapons testing
is about a third of a--

00:15:19.600 --> 00:15:21.820
or half a kilo becquerel
per square meter.

00:15:21.820 --> 00:15:22.900
I've could go look it up.

00:15:27.100 --> 00:15:28.700
If we have time,
we'll do-- let me--

00:15:28.700 --> 00:15:30.260
we'll do it at the end of class.

00:15:33.200 --> 00:15:39.380
So here's what I propose for
estimating a typical reactor

00:15:39.380 --> 00:15:40.993
accident.

00:15:40.993 --> 00:15:42.660
There's still some
Chernobyl-type things

00:15:42.660 --> 00:15:45.140
around that could
cause bad accidents.

00:15:45.140 --> 00:15:48.120
We have 450 reactors,
but 11 of these left.

00:15:48.120 --> 00:15:52.000
Let's just weight it-- a little
bit of Chernobyl in there.

00:15:52.000 --> 00:15:54.060
Not a lot of Chernobyl,
but a little bit.

00:15:54.060 --> 00:15:58.540
And then we'll have the
Fukushima, accident B,

00:15:58.540 --> 00:16:01.300
which describes most
reactors in the world.

00:16:01.300 --> 00:16:04.420
B is typical, but
we'll divide that by 3.

00:16:04.420 --> 00:16:08.140
Because it's actually
three reactor accidents--

00:16:08.140 --> 00:16:12.140
one site accident, but
three reactor accidents.

00:16:12.140 --> 00:16:15.360
So we have to make sure we
do our accounting correctly.

00:16:15.360 --> 00:16:17.180
So we'll take that
release, which 21,

00:16:17.180 --> 00:16:19.140
and we'll divide that by 3.

00:16:19.140 --> 00:16:21.740
So here's the calculation.

00:16:21.740 --> 00:16:23.540
85 becquerels times
this weighting.

00:16:23.540 --> 00:16:25.820
21 becquerels times
that weighting.

00:16:25.820 --> 00:16:29.340
And it's about 9 petabecquerels
for what I'm going

00:16:29.340 --> 00:16:32.590
to call a typical accident?

00:16:32.590 --> 00:16:33.470
Yep?

00:16:33.470 --> 00:16:35.830
AUDIENCE: Where does that
number 450 come from?

00:16:35.830 --> 00:16:36.530
What is it--

00:16:36.530 --> 00:16:38.990
R. SCOTT KEMP: Oh, total number
of reactors in the world.

00:16:38.990 --> 00:16:41.630
Yep.

00:16:41.630 --> 00:16:44.450
This is just my weighting.

00:16:44.450 --> 00:16:46.390
So this is per reactor accident.

00:16:46.390 --> 00:16:53.230
Now, it turns out that not all
accidents are simple reactor

00:16:53.230 --> 00:16:54.350
accidents.

00:16:54.350 --> 00:16:59.150
Some accidents are internal
accidents, like at Chernobyl,

00:16:59.150 --> 00:17:01.070
and some accidents
are site accidents

00:17:01.070 --> 00:17:03.270
that involve multiple reactors.

00:17:03.270 --> 00:17:07.510
So we need to figure
out how to weight them.

00:17:07.510 --> 00:17:09.010
So what I'm going
to do is just say,

00:17:09.010 --> 00:17:11.710
well, let's just
use empirical data.

00:17:11.710 --> 00:17:16.109
Barring any better data, roughly
half of them will be internal,

00:17:16.109 --> 00:17:18.724
and roughly half of
them will be external.

00:17:18.724 --> 00:17:20.349
And actually, that
makes a lot of sense

00:17:20.349 --> 00:17:23.310
from a kind of statistics
argument, in the sense

00:17:23.310 --> 00:17:27.670
that if it turned out
internal accidents dominated

00:17:27.670 --> 00:17:32.490
tremendously, and the types of
accidents of external events

00:17:32.490 --> 00:17:36.070
did not, that means you
haven't done your safety well.

00:17:36.070 --> 00:17:37.890
It means you've
underperformed in one area

00:17:37.890 --> 00:17:39.770
and overdone it in another area.

00:17:39.770 --> 00:17:43.850
So we expect these things
to be roughly the same

00:17:43.850 --> 00:17:45.810
if we design our safety.

00:17:45.810 --> 00:17:47.790
So here's my calculation--

00:17:47.790 --> 00:17:50.630
1/2 internal plus
1/2 site accident.

00:17:50.630 --> 00:17:52.250
So I'm going to
put the 3 back in.

00:17:52.250 --> 00:17:53.970
I get 18 petabecquerel.

00:17:53.970 --> 00:17:59.090
And it's about 1/5 of our
Chernobyl event, very roughly.

00:17:59.090 --> 00:18:02.770
That's what I'm going to
argue is a typical accident.

00:18:02.770 --> 00:18:04.570
You don't have to
agree with this.

00:18:04.570 --> 00:18:08.810
Do whatever you think is right
and propagate your own math.

00:18:08.810 --> 00:18:13.370
But this is just like-- this is
what the empirical history says.

00:18:13.370 --> 00:18:19.370
So once we have that
accident, then what happens?

00:18:19.370 --> 00:18:22.530
Well, there are lots
of different pathways

00:18:22.530 --> 00:18:25.050
in which you can be irradiated.

00:18:25.050 --> 00:18:30.670
You can have stuff
landing on the ground.

00:18:30.670 --> 00:18:34.070
And then it just sits there and
it glows and it irradiates you.

00:18:34.070 --> 00:18:36.070
Call this ground shine.

00:18:36.070 --> 00:18:40.950
You could inhale it because
it's floating around in the air.

00:18:40.950 --> 00:18:42.950
And that inhalation
can come directly

00:18:42.950 --> 00:18:45.670
because it's in the
air after the accident,

00:18:45.670 --> 00:18:47.030
or you kick up some dust.

00:18:47.030 --> 00:18:50.230
Roads and stuff is
constantly kicking up dust,

00:18:50.230 --> 00:18:51.670
and you Inhale it.

00:18:51.670 --> 00:18:56.670
Or it could go into the
food supply, and you eat it.

00:18:56.670 --> 00:19:00.150
So we have three
different pathways here.

00:19:00.150 --> 00:19:03.430
And it turns out
that these pathways

00:19:03.430 --> 00:19:08.190
are complicated by the
chemistry of the isotope that

00:19:08.190 --> 00:19:09.590
is being released.

00:19:09.590 --> 00:19:12.630
Once it goes into
the environment, how

00:19:12.630 --> 00:19:16.670
that isotope operates depends
on all the chemical reactions

00:19:16.670 --> 00:19:18.390
that are happening out there.

00:19:18.390 --> 00:19:20.870
So as it turns out, this
is not something you

00:19:20.870 --> 00:19:22.430
can do from first principles.

00:19:22.430 --> 00:19:29.800
You need to have basically
experimental data that tells us,

00:19:29.800 --> 00:19:32.600
on average, what does the
chemistry of the environment

00:19:32.600 --> 00:19:36.200
do to the availability
of these isotopes?

00:19:36.200 --> 00:19:39.060
So that data has been done.

00:19:39.060 --> 00:19:44.640
This is from a 1982 report
by the United Nations.

00:19:44.640 --> 00:19:53.720
And they calculate that for
every becquerel meter squared

00:19:53.720 --> 00:20:08.760
of contamination, there's 0.89,
or 9 nanograys of contamination.

00:20:08.760 --> 00:20:12.480
We want a kilobecquerel.

00:20:12.480 --> 00:20:19.520
So we actually could
state this as 9 micrograys

00:20:19.520 --> 00:20:21.700
per kilobecquerel
per meter squared.

00:20:21.700 --> 00:20:25.920
So we just go back
to our situation,

00:20:25.920 --> 00:20:32.300
we have the original
contamination

00:20:32.300 --> 00:20:36.460
is 20% of Chernobyl.

00:20:36.460 --> 00:20:40.600
The Chernobyl was 10
kilobecquerel per square meter.

00:20:46.610 --> 00:20:50.040
And now we have this
conversion factor,

00:20:50.040 --> 00:20:54.180
which is 9 microsieverts,
or 9 microgray

00:20:54.180 --> 00:20:55.820
is what it actually
says-- we'll talk

00:20:55.820 --> 00:21:01.940
about that in a second-- per
kilobecquerel per meter squared.

00:21:01.940 --> 00:21:04.860
Does that sound right?

00:21:04.860 --> 00:21:08.220
And then this is all decaying.

00:21:08.220 --> 00:21:12.300
And it's only
cesium-137, so we'll

00:21:12.300 --> 00:21:16.660
have some time dependency,
which is the half life.

00:21:16.660 --> 00:21:21.900
And then this is 30.2
years because this

00:21:21.900 --> 00:21:24.600
is the half life of cesium-137.

00:21:24.600 --> 00:21:32.240
So this is the dose
as a function of time.

00:21:32.240 --> 00:21:34.960
Does that make sense?

00:21:34.960 --> 00:21:36.460
From a typical accident?

00:21:57.540 --> 00:21:58.040
Yes?

00:22:01.487 --> 00:22:03.820
Said a typical accident is
about 1/5 fifth of Chernobyl.

00:22:03.820 --> 00:22:05.778
Chernobyl is 10 kilobecquerels
per square meter

00:22:05.778 --> 00:22:07.720
of contamination for cesium.

00:22:07.720 --> 00:22:12.480
And the dose is 9 microsieverts
per kilobecquerel per--

00:22:12.480 --> 00:22:14.140
9 microsieverts per year.

00:22:14.140 --> 00:22:14.760
I'm sorry.

00:22:14.760 --> 00:22:22.570
9 microsieverts per year per
kilobecquerel per meter squared.

00:22:22.570 --> 00:22:29.090
And then it decays, and
so there's a decay factor

00:22:29.090 --> 00:22:35.370
It turns out this number
is really important.

00:22:35.370 --> 00:22:39.190
It affects the result a lot.

00:22:39.190 --> 00:22:41.650
And it is a number that
is not fully agreed

00:22:41.650 --> 00:22:45.050
upon in the literature.

00:22:45.050 --> 00:22:49.050
I'll just briefly mention, we--

00:22:49.050 --> 00:22:53.130
I just said there's a one to
one conversion between grays

00:22:53.130 --> 00:22:56.450
and sieverts, which we know
is the relative biological

00:22:56.450 --> 00:23:00.710
effectiveness for
beta radiation.

00:23:00.710 --> 00:23:03.690
And gammas are about
the same, one to one.

00:23:03.690 --> 00:23:09.010
Technically, beta radiation
is slightly higher.

00:23:09.010 --> 00:23:12.930
But if we remember
the decay from cesium,

00:23:12.930 --> 00:23:15.610
most of the beta
energy is carried away

00:23:15.610 --> 00:23:17.250
by the antineutrino.

00:23:17.250 --> 00:23:20.390
So for the most part,
this is a gamma dose.

00:23:20.390 --> 00:23:23.650
So we really can just call
sieverts and grays the same.

00:23:27.210 --> 00:23:32.810
So 9 microsieverts is
basically what this says.

00:23:32.810 --> 00:23:37.030
Now, that's only the
ground shine dose.

00:23:37.030 --> 00:23:40.370
This is dose commitments due
to-- see the top of the slide--

00:23:40.370 --> 00:23:42.590
external irradiation.

00:23:42.590 --> 00:23:46.470
What about the stuff that
you eat or that you breathe?

00:23:46.470 --> 00:23:49.610
Well, the UN also
has data for that.

00:23:49.610 --> 00:23:53.390
They have these external
radiation inhalation ingestion

00:23:53.390 --> 00:23:54.670
in total.

00:23:54.670 --> 00:23:57.830
And so what we can
do is we can just

00:23:57.830 --> 00:24:01.990
take-- we can calculate the
other two by just taking

00:24:01.990 --> 00:24:06.190
the total, which
is given as 220,

00:24:06.190 --> 00:24:12.430
and dividing it by the
external, which is 150.

00:24:12.430 --> 00:24:14.870
And that is basically
a weighting factor

00:24:14.870 --> 00:24:30.640
that converts the external
only to the total dose

00:24:30.640 --> 00:24:33.920
from the other
ingestion pathways.

00:24:33.920 --> 00:24:37.440
People look confused.

00:24:37.440 --> 00:24:41.520
Who is slightly confused?

00:24:41.520 --> 00:24:42.060
You are.

00:24:42.060 --> 00:24:42.580
OK.

00:24:42.580 --> 00:24:47.760
So what we did is we-- the first
thing we did is we calculated--

00:24:47.760 --> 00:24:50.240
are we good up to here?

00:24:50.240 --> 00:24:52.320
OK, we're good up to
the dose coming off

00:24:52.320 --> 00:24:55.580
the ground per unit time.

00:24:55.580 --> 00:24:56.620
And then it decays.

00:24:56.620 --> 00:24:58.000
We're good with that.

00:24:58.000 --> 00:25:01.040
So now, this is just the
dose coming off the ground.

00:25:01.040 --> 00:25:06.560
And they have this chart
that says for 150 times 10

00:25:06.560 --> 00:25:11.040
to the 4 man sieverts
from external irradiation,

00:25:11.040 --> 00:25:14.040
we would have 220 total.

00:25:14.040 --> 00:25:17.460
And basically, this is
just a scaling factor.

00:25:17.460 --> 00:25:23.180
For every 150 from
external, we would have

00:25:23.180 --> 00:25:30.060
150 external plus 70 internal.

00:25:30.060 --> 00:25:33.300
150 plus 70 is 220.

00:25:33.300 --> 00:25:35.300
So it's just a scaling
factor to go up

00:25:35.300 --> 00:25:40.555
to include the effect
of the internal dose.

00:25:40.555 --> 00:25:41.180
And so I just--

00:25:41.180 --> 00:25:42.860
220 over 150.

00:25:42.860 --> 00:25:46.860
I think I hope that gets
you where we need to be.

00:25:46.860 --> 00:25:49.700
AUDIENCE: But if it's
external dose, and that

00:25:49.700 --> 00:25:52.860
comes directly from
Chernobyl, then

00:25:52.860 --> 00:25:56.500
wouldn't the amount that you
ingest be less, not more?

00:25:56.500 --> 00:25:58.100
R. SCOTT KEMP: It is much less.

00:25:58.100 --> 00:26:03.340
It's about 69.

00:26:03.340 --> 00:26:11.740
But when you add 69
plus 150, you get 220.

00:26:11.740 --> 00:26:14.333
AUDIENCE: Because that
number is only external.

00:26:14.333 --> 00:26:16.000
R. SCOTT KEMP: That
number we calculated

00:26:16.000 --> 00:26:17.740
was only the ground shine dose.

00:26:17.740 --> 00:26:19.680
That's what this plot said here.

00:26:19.680 --> 00:26:22.240
This is external irradiation.

00:26:22.240 --> 00:26:23.220
You see at the top?

00:26:23.220 --> 00:26:24.640
AUDIENCE: [INAUDIBLE].

00:26:24.640 --> 00:26:26.140
But kilometers there.

00:26:26.140 --> 00:26:28.800
But-- sorry--
kilobecquerels there.

00:26:28.800 --> 00:26:31.120
R. SCOTT KEMP: Yeah,
so I converted--

00:26:31.120 --> 00:26:44.120
so this would be 9.9 times 10
to the 8, which is 9 nanogray.

00:26:44.120 --> 00:26:50.400
And 9 nanogray per
becquerel is the same as 9

00:26:50.400 --> 00:26:52.807
microgray per kilobecquerel.

00:26:52.807 --> 00:26:53.640
AUDIENCE: All right.

00:26:53.640 --> 00:26:54.640
Thanks.

00:26:54.640 --> 00:26:57.200
R. SCOTT KEMP: Yep.

00:26:57.200 --> 00:26:59.960
Unit conversion.

00:26:59.960 --> 00:27:04.800
So this is our formula.

00:27:04.800 --> 00:27:08.480
And now we just need to say
how many people were exposed.

00:27:08.480 --> 00:27:11.320
So it turns out the
population of Europe

00:27:11.320 --> 00:27:14.610
has been very stable
for a long time--

00:27:14.610 --> 00:27:18.810
730 to 750 million people.

00:27:18.810 --> 00:27:21.530
We can basically take it as
a fixed value for the sake

00:27:21.530 --> 00:27:23.010
of our calculation.

00:27:23.010 --> 00:27:28.130
If you wanted to-- it's stable
over the lifetime of what?

00:27:28.130 --> 00:27:31.350
Over several of these,
several half lives.

00:27:31.350 --> 00:27:32.490
So 100 years.

00:27:32.490 --> 00:27:34.130
That's reasonable.

00:27:34.130 --> 00:27:36.010
If we were doing
this in Africa, we

00:27:36.010 --> 00:27:38.497
would need to have a
time-dependent population,

00:27:38.497 --> 00:27:40.330
some place where the
population dynamics are

00:27:40.330 --> 00:27:41.750
changing dramatically.

00:27:41.750 --> 00:27:44.290
But we just treat it as stable.

00:27:44.290 --> 00:27:48.470
So 750 times 10 to the 6 people.

00:27:52.970 --> 00:27:59.530
And then we're going to
integrate that from 0

00:27:59.530 --> 00:28:01.010
to infinity.

00:28:01.010 --> 00:28:03.050
Now, going to infinity
is not a big deal

00:28:03.050 --> 00:28:06.110
because almost all of it is
decayed after some half life.

00:28:06.110 --> 00:28:10.010
It just adds little
tiny bits at the end.

00:28:10.010 --> 00:28:12.170
So let's just cancel our units.

00:28:12.170 --> 00:28:14.070
Kilobecquerels cancels.

00:28:14.070 --> 00:28:15.530
Meter squares cancel.

00:28:19.110 --> 00:28:23.110
These years will cancel
with these years.

00:28:23.110 --> 00:28:26.710
And what we'll be
left with is something

00:28:26.710 --> 00:28:45.370
that has units of sieverts times
persons, something like that,

00:28:45.370 --> 00:28:48.030
what we call person sieverts.

00:28:48.030 --> 00:28:50.710
And so if you do the math,
and you do the integral,

00:28:50.710 --> 00:28:56.030
you get 860,000 person
sieverts of exposure.

00:28:56.030 --> 00:28:58.190
OK?

00:28:58.190 --> 00:28:58.910
Yep?

00:28:58.910 --> 00:28:59.577
AUDIENCE: Sorry.

00:28:59.577 --> 00:29:01.833
What does person sievert mean?

00:29:01.833 --> 00:29:03.250
R. SCOTT KEMP:
Remember, because--

00:29:03.250 --> 00:29:07.430
AUDIENCE: Sievert per
person [INAUDIBLE].

00:29:07.430 --> 00:29:09.280
R. SCOTT KEMP:
Sieverts per person--

00:29:09.280 --> 00:29:11.812
it's sieverts of dose
times the number of people.

00:29:11.812 --> 00:29:13.520
So remember, because
we're in the linear,

00:29:13.520 --> 00:29:15.440
we can use linear
no threshold model.

00:29:21.760 --> 00:29:25.520
Say, a millisievert
for 10 people

00:29:25.520 --> 00:29:29.280
would be 10 milli
person sieverts.

00:29:34.600 --> 00:29:37.960
AUDIENCE: If I have 10
millisieverts or whatever dose,

00:29:37.960 --> 00:29:41.960
and I have 10 people, I expect
that that 10 millisievert

00:29:41.960 --> 00:29:43.930
is divided by the number.

00:29:43.930 --> 00:29:45.180
R. SCOTT KEMP: No, no, no, no.

00:29:45.180 --> 00:29:47.160
AUDIENCE: [INAUDIBLE]

00:29:47.160 --> 00:29:51.272
R. SCOTT KEMP: No, because
we're not taking the radiation--

00:29:51.272 --> 00:29:53.980
That would be the case if I were
taking the radiation and saying,

00:29:53.980 --> 00:29:55.680
OK, you have a little bit,
and you can have a little bit,

00:29:55.680 --> 00:29:57.160
and you can have a little bit.

00:29:57.160 --> 00:29:58.960
But that's not what's
happening here.

00:29:58.960 --> 00:30:00.960
What's happening is I'm
spreading the radiation

00:30:00.960 --> 00:30:02.280
everywhere.

00:30:02.280 --> 00:30:04.760
We have a background
of radiation.

00:30:04.760 --> 00:30:08.960
And if I put one person there, I
get one person sievert of dose.

00:30:08.960 --> 00:30:12.060
And if I put two people in
that same field of radiation,

00:30:12.060 --> 00:30:15.193
unless they're standing so
close that their self-shielding.

00:30:15.193 --> 00:30:17.860
But as long as I have one person
here, and one person over here,

00:30:17.860 --> 00:30:20.980
and one person over here,
the more people I add,

00:30:20.980 --> 00:30:25.440
the more person sieverts
of dose I'm creating.

00:30:25.440 --> 00:30:29.360
And so I give this person
this 0.1% chance of cancer,

00:30:29.360 --> 00:30:31.120
and this person 0.1%
chance of cancer,

00:30:31.120 --> 00:30:33.200
and this 1.1% chance of cancer.

00:30:33.200 --> 00:30:35.340
And now it's total
cancers are going

00:30:35.340 --> 00:30:41.000
to be 0.1 plus 0.1
plus 0.1 total cancers.

00:30:41.000 --> 00:30:43.700
AUDIENCE: So if I take
[INAUDIBLE] millisievert,

00:30:43.700 --> 00:30:45.820
then the person next
to me [INAUDIBLE].

00:30:45.820 --> 00:30:47.700
R. SCOTT KEMP: Yes.

00:30:47.700 --> 00:30:48.740
It doesn't affect--

00:30:48.740 --> 00:30:50.380
AUDIENCE: The more I take,
the less [INAUDIBLE].

00:30:50.380 --> 00:30:51.140
R. SCOTT KEMP:
That's not-- yeah,

00:30:51.140 --> 00:30:52.360
the first description
is correct.

00:30:52.360 --> 00:30:53.610
The second one is not correct.

00:30:53.610 --> 00:30:55.260
Yeah, exactly.

00:30:55.260 --> 00:30:58.740
Because it's just
spread environmentally,

00:30:58.740 --> 00:31:01.440
not handed out like
pieces of cake.

00:31:04.740 --> 00:31:06.020
It is not yellowcake.

00:31:09.200 --> 00:31:14.760
So everyone good with
this unit, person sievert?

00:31:14.760 --> 00:31:17.400
Now we need to convert
this to cancers.

00:31:17.400 --> 00:31:19.060
So we actually know
how to do this.

00:31:19.060 --> 00:31:24.200
We looked at this
in class already.

00:31:24.200 --> 00:31:27.680
We can say-- if we have--

00:31:27.680 --> 00:31:28.700
I'll go over here.

00:31:33.320 --> 00:31:41.400
We have 860,000 person sieverts.

00:31:41.400 --> 00:31:46.800
And we saw that the excess
relative risk of cancer

00:31:46.800 --> 00:31:52.800
was 0.64 per sievert.

00:31:52.800 --> 00:31:57.640
So the excess relative risk--

00:31:57.640 --> 00:31:58.140
sorry.

00:31:58.140 --> 00:32:03.670
The excess risk is
the baseline risk.

00:32:03.670 --> 00:32:07.770
Does anyone remember what the
baseline risk is for cancer?

00:32:07.770 --> 00:32:09.130
AUDIENCE: 20%.

00:32:09.130 --> 00:32:17.610
R. SCOTT KEMP: 20%
times 0.64 per sievert.

00:32:17.610 --> 00:32:25.250
And so if we take this, and we
multiply it by 0.64 per sievert

00:32:25.250 --> 00:32:34.850
times 0.0.2 for
20%, this cancels.

00:32:34.850 --> 00:32:38.090
This is a m and this is cancers.

00:32:38.090 --> 00:32:43.690
20% is cancers per person.

00:32:43.690 --> 00:32:45.530
That's the unit for
the baseline risk.

00:32:50.450 --> 00:32:54.250
And so we have--

00:32:54.250 --> 00:32:58.890
this number-- let's
see-- person's cancer,

00:32:58.890 --> 00:33:00.710
and sieverts are canceled.

00:33:00.710 --> 00:33:03.710
So we should be able to get
the total number of cancers,

00:33:03.710 --> 00:33:14.270
which is 110,000 cancers.

00:33:14.270 --> 00:33:17.150
And you may not know
this, but I know this.

00:33:17.150 --> 00:33:19.790
About half of cancers are fatal.

00:33:19.790 --> 00:33:28.190
So this is 55,000 deaths--

00:33:28.190 --> 00:33:36.970
Europe only, cesium-137 only.

00:33:46.870 --> 00:33:50.770
We don't have to take
these people's word for it.

00:33:50.770 --> 00:33:53.270
We can also go to the
National Academies.

00:33:53.270 --> 00:33:56.010
They have this fancy supermodel.

00:33:56.010 --> 00:33:57.150
Yes?

00:33:57.150 --> 00:34:00.163
AUDIENCE: This is
per--like this accident.

00:34:00.163 --> 00:34:01.330
R. SCOTT KEMP: Per accident.

00:34:01.330 --> 00:34:03.530
Per typical accident.

00:34:03.530 --> 00:34:05.350
1/5 fifth of a Chernobyl.

00:34:05.350 --> 00:34:05.850
Yes.

00:34:09.210 --> 00:34:11.030
So you don't have
to use that plot

00:34:11.030 --> 00:34:13.489
and do it the way I just did
it from first principles.

00:34:13.489 --> 00:34:15.290
You could look up
one of these tables.

00:34:15.290 --> 00:34:18.610
They're here on page 280 of the
National Academy's committee

00:34:18.610 --> 00:34:21.130
to assess the health
risk from exposure

00:34:21.130 --> 00:34:24.010
to load levels of
ionizing radiation, which

00:34:24.010 --> 00:34:27.090
is called BEIR VII.

00:34:27.090 --> 00:34:30.730
They have this big 100,
multipage, huge document

00:34:30.730 --> 00:34:33.210
where they try to calculate
all the different risk models.

00:34:33.210 --> 00:34:34.830
And they have a
relative risk model,

00:34:34.830 --> 00:34:37.250
and they have an absolute
risk transport model.

00:34:37.250 --> 00:34:39.093
And they have it sex organized.

00:34:39.093 --> 00:34:41.010
And they have it for all
the different organs,

00:34:41.010 --> 00:34:42.750
and all these different things.

00:34:42.750 --> 00:34:45.929
And they can add it all up, and
they give you these numbers.

00:34:45.929 --> 00:34:48.150
At the end of the day,
for all solid cancers,

00:34:48.150 --> 00:34:56.929
480 per 100,000 people
exposed to 0.1 gray.

00:34:56.929 --> 00:35:01.980
So that's 480 solid cancers
in-- this is for men--

00:35:01.980 --> 00:35:05.860
per 10,000 person gray.

00:35:05.860 --> 00:35:07.540
And here, we have
the same thing.

00:35:07.540 --> 00:35:09.240
704-- sorry, ladies.

00:35:09.240 --> 00:35:13.300
You're much more likely to die.

00:35:13.300 --> 00:35:14.720
This also is not cancers.

00:35:14.720 --> 00:35:16.080
This goes directly to mortality.

00:35:16.080 --> 00:35:17.260
You see at the top--

00:35:17.260 --> 00:35:18.480
solid cancer mortality.

00:35:18.480 --> 00:35:21.740
So this is their statistical
data on just mortality.

00:35:21.740 --> 00:35:27.980
740 per 10,000 person gray.

00:35:27.980 --> 00:35:29.300
And if we add averages.

00:35:29.300 --> 00:35:32.620
We say roughly, it's
50% men and women.

00:35:32.620 --> 00:35:36.580
Then 610 is the average
of these two numbers.

00:35:36.580 --> 00:35:42.740
610 deaths per
100,000 person gray.

00:35:42.740 --> 00:35:44.600
So let's do that here.

00:35:52.500 --> 00:36:01.520
610 deaths per
100,000 person gray.

00:36:01.520 --> 00:36:04.240
And how many person
gray did we have?

00:36:04.240 --> 00:36:10.480
860,000 person gray,
which is 86 times 110,000.

00:36:10.480 --> 00:36:13.126
So times 86--

00:36:13.126 --> 00:36:17.520
860,000 person grays.

00:36:17.520 --> 00:36:26.560
And 610 times 86 is,
I think, 520 deaths.

00:36:26.560 --> 00:36:30.360
So it basically matches
that calculation.

00:36:30.360 --> 00:36:33.720
That's nice to know
that they both match.

00:36:33.720 --> 00:36:38.560
So pretty close.

00:36:38.560 --> 00:36:44.440
So this is only cesium.

00:36:44.440 --> 00:36:45.860
Was this what?

00:36:45.860 --> 00:36:47.080
AUDIENCE: [INAUDIBLE]

00:36:47.080 --> 00:36:48.540
R. SCOTT KEMP: Oh, no.

00:36:52.920 --> 00:36:54.340
That is wrong by--

00:36:56.970 --> 00:37:01.850
that is wrong by my math.

00:37:01.850 --> 00:37:07.550
What is 600-- they're not
off by a factor of 10.

00:37:07.550 --> 00:37:08.510
What am I doing wrong?

00:37:08.510 --> 00:37:12.906
AUDIENCE: A hundred
[? thousands. ?]

00:37:23.810 --> 00:37:25.310
R. SCOTT KEMP: Who
has a calculator?

00:37:27.930 --> 00:37:30.210
86 times 610.

00:37:30.210 --> 00:37:33.108
AUDIENCE: [INAUDIBLE]

00:37:35.657 --> 00:37:36.490
R. SCOTT KEMP: Typo.

00:37:39.570 --> 00:37:41.610
Yeah, they match.

00:37:41.610 --> 00:37:43.790
If they didn't match, I
wouldn't have presented it.

00:37:47.090 --> 00:37:49.270
52,000 deaths, not
500,000 deaths.

00:37:49.270 --> 00:37:52.190
52,000 deaths.

00:37:52.190 --> 00:37:54.650
So that was only-- this
is only from cesium.

00:37:54.650 --> 00:37:58.510
This is only in Europe
from a typical accident.

00:37:58.510 --> 00:38:00.430
So I mentioned that
the other thing

00:38:00.430 --> 00:38:02.590
that we have to really
worry about is iodine.

00:38:02.590 --> 00:38:05.790
And so let's just look at
what the situation was iodine.

00:38:05.790 --> 00:38:07.910
This is from an UNSCEAR report.

00:38:07.910 --> 00:38:10.670
And what they do
is they actually--

00:38:10.670 --> 00:38:13.970
they carefully calculate all
the iodine exposure out there.

00:38:13.970 --> 00:38:16.630
There's a lot of
experimental assessment.

00:38:16.630 --> 00:38:20.930
And they have categories of
evacuees, recovery workers,

00:38:20.930 --> 00:38:24.630
inhabitants of Belarus,
Russia, and Ukraine,

00:38:24.630 --> 00:38:26.610
and inhabitants of
distant countries.

00:38:26.610 --> 00:38:29.350
And they figure it all
out what the dosing is.

00:38:29.350 --> 00:38:32.650
And they have the collective
thyroid dose only in 1986,

00:38:32.650 --> 00:38:35.830
because it doesn't
really last that long.

00:38:35.830 --> 00:38:37.810
And they find if you
add all these up,

00:38:37.810 --> 00:38:42.070
it's about 3 million
person sieverts.

00:38:42.070 --> 00:38:47.830
And they have also the effective
dose, not to the thyroid,

00:38:47.830 --> 00:38:49.750
to other parts of your body.

00:38:49.750 --> 00:38:53.170
And it's about 380,000
person sieverts.

00:38:53.170 --> 00:38:58.490
So this is about 3.4, Something
Like 3.4 million person

00:38:58.490 --> 00:38:59.933
sieverts of dose from iodine.

00:38:59.933 --> 00:39:01.850
And we don't have to do
this whole decay thing

00:39:01.850 --> 00:39:03.310
because they've done all that.

00:39:03.310 --> 00:39:05.330
This thing is
decayed all the way,

00:39:05.330 --> 00:39:07.810
and they're just giving
you the final dose.

00:39:07.810 --> 00:39:09.290
So here it is.

00:39:09.290 --> 00:39:14.930
Here's the dose from Chernobyl.

00:39:14.930 --> 00:39:16.510
Here's the dose from cesium.

00:39:16.510 --> 00:39:17.970
Here's the dose from iodine.

00:39:17.970 --> 00:39:20.230
Here's some other isotopes
that we could look at.

00:39:20.230 --> 00:39:23.090
And if I just rescale them
all to our typical accident,

00:39:23.090 --> 00:39:24.510
here they are, rescaled.

00:39:27.890 --> 00:39:29.410
So I can add them
all up together.

00:39:29.410 --> 00:39:30.910
There are a bunch
of other isotopes,

00:39:30.910 --> 00:39:32.097
and they get really tiny.

00:39:32.097 --> 00:39:33.430
So we don't have to worry about.

00:39:33.430 --> 00:39:35.770
So let's just take the top four.

00:39:35.770 --> 00:39:39.090
And it turns out 2.3 million
person sieverts is the total

00:39:39.090 --> 00:39:44.010
dose instead of 860,000, which
means it's about 2.7 times

00:39:44.010 --> 00:39:50.100
higher than we calculated
for total deaths.

00:39:50.100 --> 00:39:51.932
Yes?

00:39:51.932 --> 00:39:53.640
Everyone understand
what's going on here?

00:39:53.640 --> 00:39:56.380
So we're just basically
going from one isotope,

00:39:56.380 --> 00:39:58.620
and then I've done
the same stuff

00:39:58.620 --> 00:40:00.900
for the other isotopes for you.

00:40:00.900 --> 00:40:05.220
And we can just go to
the all isotope dose.

00:40:05.220 --> 00:40:11.940
And then UNSCEAR estimates
that for Chernobyl, they

00:40:11.940 --> 00:40:14.780
estimated 10 million
person sieverts of dose

00:40:14.780 --> 00:40:17.532
to all Europeans, 16
million person sieverts

00:40:17.532 --> 00:40:18.240
to all the world.

00:40:18.240 --> 00:40:21.500
So their multiplier to go from
Europe to the rest of the world

00:40:21.500 --> 00:40:23.340
was a factor of 1.6.

00:40:23.340 --> 00:40:26.220
I earlier made
the argument using

00:40:26.220 --> 00:40:30.300
that Fukushima map that it
was roughly a factor of 2.

00:40:30.300 --> 00:40:32.900
This is a little bit
more conservative,

00:40:32.900 --> 00:40:35.420
so let's use this number.

00:40:35.420 --> 00:40:40.220
So we would take our calculation
of 55,000, or 52,000, deaths,

00:40:40.220 --> 00:40:44.540
and we would multiply it by
2.7, and multiply it by 1.6.

00:40:44.540 --> 00:40:49.640
So I average those together
and suggested we use 53,000,

00:40:49.640 --> 00:40:56.960
and times 2.7 times 1.6, which
gives us 230,000 deaths per

00:40:56.960 --> 00:41:02.570
typical major accident
worldwide, all isotopes.

00:41:02.570 --> 00:41:03.560
Yes?

00:41:03.560 --> 00:41:04.680
AUDIENCE: And then what--
are we going to multiply that

00:41:04.680 --> 00:41:06.082
by the frequency of accidents?

00:41:06.082 --> 00:41:07.040
R. SCOTT KEMP: Correct.

00:41:07.040 --> 00:41:07.920
Yeah.

00:41:07.920 --> 00:41:12.320
So this is the basic result that
you should have in your mind.

00:41:12.320 --> 00:41:17.240
The average large INES 7--

00:41:17.240 --> 00:41:18.720
average according
to this weighting

00:41:18.720 --> 00:41:20.320
that I showed you earlier--

00:41:20.320 --> 00:41:24.040
accident kills a quarter
million people from cancer

00:41:24.040 --> 00:41:26.120
and gives another
quarter million people

00:41:26.120 --> 00:41:29.120
cancer that doesn't kill them.

00:41:29.120 --> 00:41:30.780
And that's only
the cancer effects.

00:41:30.780 --> 00:41:34.160
This is not the teratogenic
effects and inheritable defects,

00:41:34.160 --> 00:41:39.800
the deterministic diseases, all
the other stuff, heart disease,

00:41:39.800 --> 00:41:41.300
et cetera.

00:41:41.300 --> 00:41:43.780
All the other all-hazard
mortality is not included.

00:41:43.780 --> 00:41:46.250
This is only cancer deaths.

00:41:46.250 --> 00:41:48.910
But it's a big source of death.

00:41:48.910 --> 00:41:53.330
So it's a good number to go on.

00:41:53.330 --> 00:41:57.570
So quarter million people--
now, that sounds like a lot.

00:41:57.570 --> 00:41:59.330
That sounds like a lot.

00:41:59.330 --> 00:42:02.570
But you have to remember that
coal is killing people all

00:42:02.570 --> 00:42:07.610
the time, and you just don't
see these deaths from PM10,

00:42:07.610 --> 00:42:10.770
to PM2.5, from radiation
from coal, et cetera.

00:42:10.770 --> 00:42:13.370
So we really don't
know yet whether this

00:42:13.370 --> 00:42:15.390
is a big-- it's a
very dramatic number,

00:42:15.390 --> 00:42:19.250
but we don't know if
on average is big yet.

00:42:19.250 --> 00:42:21.710
AUDIENCE: So what is the
time frame for these deaths?

00:42:21.710 --> 00:42:26.370
Because it's not clear
to me whether this

00:42:26.370 --> 00:42:32.553
means there'll be a quarter of a
million deaths in month after--

00:42:32.553 --> 00:42:33.470
R. SCOTT KEMP: No, no.

00:42:33.470 --> 00:42:34.870
They are spread out.

00:42:34.870 --> 00:42:35.810
AUDIENCE: --20 years.

00:42:35.810 --> 00:42:38.730
R. SCOTT KEMP: They're
spread out over 100 years.

00:42:38.730 --> 00:42:39.450
Yeah.

00:42:39.450 --> 00:42:44.670
They just appear as people
who just got cancer.

00:42:44.670 --> 00:42:47.150
This is your aunt
who got cancer.

00:42:47.150 --> 00:42:49.790
Why did they get cancer?

00:42:49.790 --> 00:42:53.590
And for some small fraction
of the population, the reason

00:42:53.590 --> 00:42:59.950
they got cancer was
radiation from cesium-137

00:42:59.950 --> 00:43:02.990
that just happened to shoot
a photon into their body

00:43:02.990 --> 00:43:05.790
and break the genome
in the wrong way.

00:43:05.790 --> 00:43:07.070
And you can't tell.

00:43:07.070 --> 00:43:10.950
There's no way that
you can figure it out.

00:43:10.950 --> 00:43:14.110
And then because the
background rate of cancers

00:43:14.110 --> 00:43:18.030
is already 1 in 5
persons, this is really

00:43:18.030 --> 00:43:22.030
just a tiny perturbation
on that background.

00:43:22.030 --> 00:43:24.410
If you have 10 billion
people, and 1/5 of them,

00:43:24.410 --> 00:43:27.390
2 billion people, are
going to get cancer,

00:43:27.390 --> 00:43:29.630
this is a tiny perturbation.

00:43:29.630 --> 00:43:31.950
You can't see it.

00:43:31.950 --> 00:43:35.110
So that's the problem, is
that you can't empirically

00:43:35.110 --> 00:43:37.870
see these deaths,
but they're there.

00:43:37.870 --> 00:43:40.770
They are caused by the accident.

00:43:40.770 --> 00:43:41.270
Yeah?

00:43:41.270 --> 00:43:43.103
AUDIENCE: So how do we
measure the, I guess,

00:43:43.103 --> 00:43:45.850
the frequency if the
events are so sparse?

00:43:45.850 --> 00:43:47.032
[INAUDIBLE]

00:43:47.032 --> 00:43:48.490
R. SCOTT KEMP:
Well, that goes back

00:43:48.490 --> 00:43:50.690
to how did we get the
dose response model?

00:43:50.690 --> 00:43:55.770
And that is basically this
study, the atomic bomb survivors

00:43:55.770 --> 00:43:57.330
plus radiation
workers, people who

00:43:57.330 --> 00:44:01.290
have higher doses, where
we then build a model

00:44:01.290 --> 00:44:03.090
to see what those doses do.

00:44:03.090 --> 00:44:04.950
And we had this
in the last class.

00:44:04.950 --> 00:44:09.570
We talked about why that model
is only defensibly linear,

00:44:09.570 --> 00:44:13.190
and why we don't have
a fancier model for it.

00:44:13.190 --> 00:44:15.830
AUDIENCE: So we have the 230,000
deaths from a major accident,

00:44:15.830 --> 00:44:17.850
and I guess, how do
we get that like a--

00:44:17.850 --> 00:44:20.987
can we give that as a per year?

00:44:20.987 --> 00:44:22.070
R. SCOTT KEMP: Well, yeah.

00:44:22.070 --> 00:44:27.370
You could assume that
the deaths expose people

00:44:27.370 --> 00:44:29.690
according to the decay,
so that most people are

00:44:29.690 --> 00:44:31.330
exposed right away.

00:44:31.330 --> 00:44:34.610
But then there's some time
between when those people are

00:44:34.610 --> 00:44:37.230
exposed and when they become--
when they die from cancer.

00:44:37.230 --> 00:44:39.290
And that could be 10 years.

00:44:39.290 --> 00:44:42.420
So there's this smearing--

00:44:42.420 --> 00:44:43.685
a delay and smearing.

00:44:43.685 --> 00:44:45.060
AUDIENCE: [INAUDIBLE]
get rid of.

00:44:45.060 --> 00:44:46.643
Like, if we were
trying-- if we really

00:44:46.643 --> 00:44:48.100
wanted a per year [INAUDIBLE].

00:44:48.100 --> 00:44:52.130
R. SCOTT KEMP: Order
of magnitude from 1--

00:44:52.130 --> 00:44:53.880
AUDIENCE: [INAUDIBLE]
like over 100 years.

00:44:53.880 --> 00:44:55.380
But like, obviously, you
can't [? divide by-- ?]

00:44:55.380 --> 00:44:56.020
R. SCOTT KEMP: So it depends.

00:44:56.020 --> 00:44:57.900
If you're assuming there's a
constant rate of accidents,

00:44:57.900 --> 00:44:59.360
or are you assuming
one accident?

00:44:59.360 --> 00:45:01.527
AUDIENCE: If we're trying
to say there's a certain--

00:45:01.527 --> 00:45:04.000
how people do [INAUDIBLE]--
totally other thing.

00:45:04.000 --> 00:45:08.580
But if you have an accident
rate per year, what would

00:45:08.580 --> 00:45:10.855
that relative [INAUDIBLE]?

00:45:10.855 --> 00:45:12.340
We're trying to get that--

00:45:12.340 --> 00:45:12.980
R. SCOTT KEMP: Then
we're going to get

00:45:12.980 --> 00:45:14.640
to an accident rate per year.

00:45:14.640 --> 00:45:16.598
So maybe it will
answer your question.

00:45:16.598 --> 00:45:17.140
AUDIENCE: OK.

00:45:17.140 --> 00:45:17.620
R. SCOTT KEMP: Yeah.

00:45:17.620 --> 00:45:18.140
Yeah?

00:45:18.140 --> 00:45:19.848
AUDIENCE: Maybe this
is a naive question.

00:45:19.848 --> 00:45:23.380
But if you can't
differentiate, how do you

00:45:23.380 --> 00:45:26.058
pick a background cancer rate?

00:45:26.058 --> 00:45:28.100
R. SCOTT KEMP: The background
cancer rate is just

00:45:28.100 --> 00:45:31.540
the number of people who live--

00:45:31.540 --> 00:45:33.560
who die versus the
number of people--

00:45:33.560 --> 00:45:33.580
AUDIENCE: [INAUDIBLE].

00:45:33.580 --> 00:45:34.540
So it has nothing
to do with how you

00:45:34.540 --> 00:45:35.990
delineate where it came from.

00:45:35.990 --> 00:45:36.740
R. SCOTT KEMP: No.

00:45:36.740 --> 00:45:37.240
Yeah.

00:45:37.240 --> 00:45:39.460
It's just the number of
people who die from cancer.

00:45:39.460 --> 00:45:39.960
Yeah.

00:45:39.960 --> 00:45:42.690
Yeah?

00:45:42.690 --> 00:45:44.440
AUDIENCE: I guess it
maybe kind of relates

00:45:44.440 --> 00:45:47.000
to previous
questions, but how do

00:45:47.000 --> 00:45:50.180
we put this in perspective
related to the background?

00:45:50.180 --> 00:45:53.240
Because if we look at 10
kilobecquerels per square meters

00:45:53.240 --> 00:45:55.120
times roughly 10
microsieverts per,

00:45:55.120 --> 00:45:58.332
it's like 1 millisievert per
year that you get from this.

00:45:58.332 --> 00:46:00.040
I quickly looked up,
what's the variation

00:46:00.040 --> 00:46:01.680
in background rate in Europe.

00:46:01.680 --> 00:46:04.895
It's anywhere between
1.5 to 5.8 millisieverts.

00:46:04.895 --> 00:46:07.020
It's like all of this
disappears in the background.

00:46:07.020 --> 00:46:07.800
R. SCOTT KEMP: That's correct.

00:46:07.800 --> 00:46:09.217
AUDIENCE: [INAUDIBLE]
doesn't show

00:46:09.217 --> 00:46:11.440
that the Netherlands, which
apparently has the lowest

00:46:11.440 --> 00:46:14.580
background radiation, has
significantly less cancer.

00:46:14.580 --> 00:46:16.640
So is the problem,
then, that we're

00:46:16.640 --> 00:46:20.680
kind of including radiation
effects in the relative risk

00:46:20.680 --> 00:46:22.940
background, and that's
why everything is here?

00:46:22.940 --> 00:46:27.120
But why don't we see in
LNT a more drastic change

00:46:27.120 --> 00:46:29.820
in cancer rates than
between the Czech Republic,

00:46:29.820 --> 00:46:32.080
[INAUDIBLE] is
5.8 millisieverts,

00:46:32.080 --> 00:46:37.820
and then the Netherlands is 1.5,
if 0.1 millisieverts per year

00:46:37.820 --> 00:46:41.180
creates such a drastic
difference [INAUDIBLE].

00:46:41.180 --> 00:46:45.540
R. SCOTT KEMP: So I
think you're asking--

00:46:45.540 --> 00:46:48.120
regional variation and
background can be, let's say,

00:46:48.120 --> 00:46:50.860
factors of 2, factors of 3.

00:46:50.860 --> 00:46:54.780
Certain very small
regions are higher.

00:46:54.780 --> 00:46:58.140
And yet, you don't see factors
of 2 difference in the cancer

00:46:58.140 --> 00:47:00.160
rate in those regions.

00:47:00.160 --> 00:47:03.380
That's because most cancers
are not caused by radiation.

00:47:03.380 --> 00:47:07.340
Most cancers are caused by just
oxidation stress in the body,

00:47:07.340 --> 00:47:09.620
by crap you're eating,
by whether you're

00:47:09.620 --> 00:47:11.020
smoking cigarettes.

00:47:11.020 --> 00:47:13.900
So already, the
radiation-induced cancers

00:47:13.900 --> 00:47:16.460
are already in the noise.

00:47:16.460 --> 00:47:21.540
These are also in the noise,
but they're not there.

00:47:21.540 --> 00:47:25.140
They are in the noise,
but they're there.

00:47:25.140 --> 00:47:29.540
So it is incorrect to say,
oh, well, lots of people

00:47:29.540 --> 00:47:30.240
die from cancer.

00:47:30.240 --> 00:47:32.220
Therefore, we
should ignore this.

00:47:32.220 --> 00:47:38.990
Well, this accident did kill
an additional 52,000 people.

00:47:38.990 --> 00:47:40.670
That happened.

00:47:40.670 --> 00:47:45.010
Now, you can-- or in this
case, quarter million people

00:47:45.010 --> 00:47:48.360
once we do all the calculation.

00:47:48.360 --> 00:47:53.630
Yes, the background is noisy
and big, and everyone dies.

00:47:53.630 --> 00:47:57.590
But to say that
it's insignificant

00:47:57.590 --> 00:48:00.550
is incorrect, if I can take
that same energy source

00:48:00.550 --> 00:48:04.350
and replace it with something
that doesn't cause any deaths,

00:48:04.350 --> 00:48:07.130
or many fewer deaths.

00:48:07.130 --> 00:48:12.450
So it doesn't go away just
because you can't see it.

00:48:15.190 --> 00:48:18.150
Because someone doesn't show up
in the hospital, and they go,

00:48:18.150 --> 00:48:20.910
oh, this is a Chernobyl cancer.

00:48:20.910 --> 00:48:24.602
If we could do that,
if we had the science--

00:48:24.602 --> 00:48:26.810
everyone shows up at oncology,
and they go, oh, yeah,

00:48:26.810 --> 00:48:31.870
this is from Fukushima, then
the news reports would say,

00:48:31.870 --> 00:48:35.690
another 10,000 people died
from Fukushima this year,

00:48:35.690 --> 00:48:39.610
and people would go crazy.

00:48:39.610 --> 00:48:41.490
It's the fact that
we get to hide them

00:48:41.490 --> 00:48:44.790
that we don't have to take
accountability for them,

00:48:44.790 --> 00:48:46.265
but they're still there.

00:48:46.265 --> 00:48:46.890
AUDIENCE: Yeah.

00:48:46.890 --> 00:48:48.307
I mean, the question
was more, why

00:48:48.307 --> 00:48:51.190
does an LNT show a difference
in background between countries

00:48:51.190 --> 00:48:52.190
if it's so much smaller?

00:48:52.190 --> 00:48:54.690
R. SCOTT KEMP: But the answer
is because most of the cancers

00:48:54.690 --> 00:48:55.730
are not from radiation.

00:48:55.730 --> 00:48:57.240
Yeah.

00:48:57.240 --> 00:48:58.990
AUDIENCE: I was just
going to [INAUDIBLE].

00:48:58.990 --> 00:49:03.770
Do you use similar models to
analyze the amount of deaths

00:49:03.770 --> 00:49:05.430
related to cancer
or other factors--

00:49:05.430 --> 00:49:10.530
respiratory or cardiovascular
or fossil fuels

00:49:10.530 --> 00:49:13.490
and natural gas and other
types of energy sources?

00:49:13.490 --> 00:49:16.170
Or they would you use a
different type of model.

00:49:16.170 --> 00:49:19.090
R. SCOTT KEMP: You can
only do such an easy model

00:49:19.090 --> 00:49:22.690
if there's a linear
relationship between exposure

00:49:22.690 --> 00:49:25.330
and pathogenesis.

00:49:25.330 --> 00:49:28.970
So for a lot of diseases,
which are not stochastic,

00:49:28.970 --> 00:49:31.050
which don't have a
linear relationship,

00:49:31.050 --> 00:49:33.620
it will depend on
thresholds, or there will

00:49:33.620 --> 00:49:35.160
be some nonlinear curvature.

00:49:35.160 --> 00:49:37.118
And that means you're
going to have a much more

00:49:37.118 --> 00:49:38.765
sophisticated calculation of--

00:49:38.765 --> 00:49:39.640
AUDIENCE: [INAUDIBLE]

00:49:39.640 --> 00:49:40.420
R. SCOTT KEMP: Yeah, exactly.

00:49:40.420 --> 00:49:42.940
How many people from this
plant, and how many people live

00:49:42.940 --> 00:49:45.500
downwind of that particular
plant of coal plant

00:49:45.500 --> 00:49:48.640
or something, and
breathe that PM2.5.

00:49:48.640 --> 00:49:50.940
And yeah, so it's a
lot more complicated.

00:49:50.940 --> 00:49:55.780
We actually get off easy
because of the LNT model

00:49:55.780 --> 00:49:57.160
in doing this calculation.

00:49:57.160 --> 00:49:59.340
Yeah.

00:49:59.340 --> 00:49:59.840
All right.

00:49:59.840 --> 00:50:01.440
So let me keep going.

00:50:04.260 --> 00:50:08.280
So we've added the iodine,
and we have this global dose,

00:50:08.280 --> 00:50:15.820
and the question is, do
we believe Scott's number?

00:50:15.820 --> 00:50:16.900
I mean--

00:50:16.900 --> 00:50:18.140
AUDIENCE: I will say no.

00:50:18.140 --> 00:50:19.120
No, I don't.

00:50:19.120 --> 00:50:23.080
But I take umbrage with the
linear no-threshold model.

00:50:23.080 --> 00:50:26.020
I'm more in favor of the
linear threshold model.

00:50:26.020 --> 00:50:28.620
R. SCOTT KEMP: Did
you come to class?

00:50:28.620 --> 00:50:29.900
AUDIENCE: Yeah.

00:50:29.900 --> 00:50:31.240
Well, I wasn't there last time.

00:50:31.240 --> 00:50:32.360
I was [INAUDIBLE].

00:50:32.360 --> 00:50:33.440
R. SCOTT KEMP: OK.

00:50:33.440 --> 00:50:35.200
AUDIENCE: But the--

00:50:35.200 --> 00:50:36.747
I mean, [INAUDIBLE].

00:50:36.747 --> 00:50:37.580
R. SCOTT KEMP: Yeah.

00:50:37.580 --> 00:50:39.820
So this is where things
start to go wrong.

00:50:39.820 --> 00:50:41.500
People are like, oh,
I hate this number.

00:50:41.500 --> 00:50:43.840
Now I'm going to
choose not to believe

00:50:43.840 --> 00:50:47.240
the linear no-threshold model
because it saves me from having

00:50:47.240 --> 00:50:48.320
to deal with this number.

00:50:48.320 --> 00:50:48.820
I'm sorry.

00:50:48.820 --> 00:50:50.680
That's not scientific.

00:50:50.680 --> 00:50:53.280
You don't just get to pick a
model that is not statistically

00:50:53.280 --> 00:50:56.400
defensible because you
don't like the result.

00:50:56.400 --> 00:51:00.160
So I appreciate that people
do this all the time,

00:51:00.160 --> 00:51:04.140
but we're not going
to do that here.

00:51:04.140 --> 00:51:04.640
All right.

00:51:04.640 --> 00:51:06.480
Two more questions,
then I need to move on.

00:51:06.480 --> 00:51:08.480
AUDIENCE: I was going to
say, does it really matter?

00:51:08.480 --> 00:51:10.688
If we know-- if there was
some theoretical threshold,

00:51:10.688 --> 00:51:14.382
if it was really small, how much
does that really affect the--

00:51:14.382 --> 00:51:16.840
would it be magnitudes, or if
it's a threshold that small--

00:51:16.840 --> 00:51:21.453
R. SCOTT KEMP: It could
have a significant effect.

00:51:21.453 --> 00:51:23.120
I don't know if
magnitudes, but it could

00:51:23.120 --> 00:51:24.500
have a significant effect.

00:51:24.500 --> 00:51:26.560
But the argument, the
mechanistic argument

00:51:26.560 --> 00:51:29.380
against the threshold,
remember, is the fact

00:51:29.380 --> 00:51:31.740
that in low LET
radiation transport,

00:51:31.740 --> 00:51:34.360
you have Compton scattering
and photoelectric effect.

00:51:34.360 --> 00:51:35.540
So you have these chains.

00:51:35.540 --> 00:51:37.040
You can create
double strand breaks.

00:51:37.040 --> 00:51:39.980
Double strand breaks are
basically difficult to repair.

00:51:39.980 --> 00:51:43.940
A single photon can cause a
poorly repaired double strand

00:51:43.940 --> 00:51:46.180
break that then causes cancer.

00:51:46.180 --> 00:51:49.820
As long as that chain
of physics is possible,

00:51:49.820 --> 00:51:54.300
there cannot be a threshold.

00:51:54.300 --> 00:51:58.880
So I don't see any basis for
believing there's a threshold.

00:51:58.880 --> 00:52:01.300
It's neither
empirically defensible

00:52:01.300 --> 00:52:03.040
nor mechanistically defensible.

00:52:05.706 --> 00:52:06.640
Yes?

00:52:06.640 --> 00:52:09.360
AUDIENCE: With such a marginal
change from background

00:52:09.360 --> 00:52:11.460
having [INAUDIBLE]
effect, I wonder

00:52:11.460 --> 00:52:17.620
how this would stack up
against other industries that

00:52:17.620 --> 00:52:19.260
cause harm, arguably.

00:52:19.260 --> 00:52:22.100
How would this compare to
the increase in deaths caused

00:52:22.100 --> 00:52:23.870
by McDonald's, [INAUDIBLE]?

00:52:23.870 --> 00:52:24.620
R. SCOTT KEMP: Oh.

00:52:24.620 --> 00:52:25.975
Probably-- yeah.

00:52:25.975 --> 00:52:26.600
AUDIENCE: Tiny.

00:52:26.600 --> 00:52:27.683
R. SCOTT KEMP: Tiny, yeah.

00:52:27.683 --> 00:52:30.070
No, there are--
driving your car,

00:52:30.070 --> 00:52:33.510
eating peanut butter,
which contains aflatoxin,

00:52:33.510 --> 00:52:36.350
choosing to walk on the side
of the road versus not walking

00:52:36.350 --> 00:52:39.470
on the side of the road, wearing
a bicycle helmet-- these things

00:52:39.470 --> 00:52:42.750
have huge impacts on mortality.

00:52:42.750 --> 00:52:43.830
Yeah?

00:52:43.830 --> 00:52:48.710
AUDIENCE: So your point isn't
that this number should then

00:52:48.710 --> 00:52:51.910
be used to justify or not
justify nuclear, but instead,

00:52:51.910 --> 00:52:53.070
be used for comparison.

00:52:53.070 --> 00:52:54.670
R. SCOTT KEMP: Only that.

00:52:54.670 --> 00:52:56.870
You can only take
this and compare it

00:52:56.870 --> 00:53:00.630
to other technologies which are
also killing you in other ways.

00:53:00.630 --> 00:53:02.510
That's all you can use this for.

00:53:02.510 --> 00:53:03.110
Yeah.

00:53:03.110 --> 00:53:06.310
This is not-- because
250,000 feels big,

00:53:06.310 --> 00:53:07.930
it's not an argument
against nuclear.

00:53:07.930 --> 00:53:09.810
Let's be really
clear about that.

00:53:09.810 --> 00:53:13.190
It is not an argument
against nuclear.

00:53:13.190 --> 00:53:17.070
And in the last half hour, I
want to get to that comparison.

00:53:17.070 --> 00:53:18.497
Yeah?

00:53:18.497 --> 00:53:20.830
AUDIENCE: This is really only
for comparing other energy

00:53:20.830 --> 00:53:21.330
forms.

00:53:21.330 --> 00:53:22.750
We can't compare
this number to--

00:53:22.750 --> 00:53:24.790
R. SCOTT KEMP: Peanut butter.

00:53:24.790 --> 00:53:25.290
Correct.

00:53:25.290 --> 00:53:26.950
Because they're
not a substitution.

00:53:26.950 --> 00:53:30.650
But we can compare it to other
forms of electricity generation,

00:53:30.650 --> 00:53:32.530
and that's what we
should be doing.

00:53:32.530 --> 00:53:34.090
So let's do it.

00:53:34.090 --> 00:53:38.450
So first, I want to talk a
little bit about whether we

00:53:38.450 --> 00:53:39.310
believe this number.

00:53:39.310 --> 00:53:41.690
Because how many people have
heard 4,000 people died from

00:53:41.690 --> 00:53:43.790
Chernobyl?

00:53:43.790 --> 00:53:44.290
Yeah.

00:53:44.290 --> 00:53:44.870
OK.

00:53:44.870 --> 00:53:47.050
Where did that come from?

00:53:47.050 --> 00:53:50.330
So here are the
published estimates--

00:53:50.330 --> 00:53:53.390
4,000 deaths, 9,000 deaths,
16,000 deaths, 40,000 deaths,

00:53:53.390 --> 00:53:56.890
60,000 deaths, 270,000 deaths.

00:53:56.890 --> 00:54:00.410
But you have to look at
what is being assumed.

00:54:00.410 --> 00:54:03.190
Only the most exposed
cohort of people,

00:54:03.190 --> 00:54:04.890
and only in three countries.

00:54:04.890 --> 00:54:07.350
Same people-- this is where
the 4,000 deaths come from.

00:54:07.350 --> 00:54:11.110
It was a study done by
the UN Chernobyl people.

00:54:11.110 --> 00:54:12.570
It was actually
done pretty shortly

00:54:12.570 --> 00:54:15.450
after it was reported in 2005.

00:54:15.450 --> 00:54:18.510
Then they said, oh,
we'll look at all people,

00:54:18.510 --> 00:54:20.990
not just like the most
exposed populations.

00:54:20.990 --> 00:54:23.620
And then that number
went up to 9,000.

00:54:23.620 --> 00:54:27.220
Then the World Health
Organization research on cancer

00:54:27.220 --> 00:54:31.020
came up with a
number up until 2065.

00:54:31.020 --> 00:54:35.180
Only Europe of 16,000.

00:54:35.180 --> 00:54:38.340
A group of independent
scientists out of the UK

00:54:38.340 --> 00:54:40.700
didn't like the
stuff that the UN

00:54:40.700 --> 00:54:44.340
was doing, with only reporting
subsets of the population,

00:54:44.340 --> 00:54:46.400
and only the people in
these three countries.

00:54:46.400 --> 00:54:48.360
And they felt this was unfair.

00:54:48.360 --> 00:54:50.260
So they produced these reports.

00:54:50.260 --> 00:54:52.440
One in 2006, and one in 2016--

00:54:52.440 --> 00:54:54.540
40,000 and 60,000.

00:54:54.540 --> 00:54:56.480
This one is still
limited to Europe.

00:54:56.480 --> 00:54:58.140
This one is global.

00:54:58.140 --> 00:55:01.860
And then you have this
Greenpeace report--

00:55:01.860 --> 00:55:03.900
270,000.

00:55:03.900 --> 00:55:08.460
So all of these credible
people come out less.

00:55:08.460 --> 00:55:14.140
Roughly, one fourth to
one fifth of the number

00:55:14.140 --> 00:55:16.100
that I came up with.

00:55:16.100 --> 00:55:18.820
So why is that?

00:55:18.820 --> 00:55:23.960
So the answer is that they use
a 1980s US Department of Energy

00:55:23.960 --> 00:55:27.120
report on the contamination
to dose factor.

00:55:27.120 --> 00:55:28.300
That is, this factor.

00:55:28.300 --> 00:55:29.260
Remember this?

00:55:29.260 --> 00:55:31.440
And I said this
was controversial.

00:55:31.440 --> 00:55:36.320
They used a number
that reads 0.2 here.

00:55:36.320 --> 00:55:39.840
That 1980s report doesn't have
any justification for that

00:55:39.840 --> 00:55:40.340
number.

00:55:40.340 --> 00:55:42.560
They just tabulate numbers
for a bunch of isotopes,

00:55:42.560 --> 00:55:44.400
and that's it.

00:55:44.400 --> 00:55:46.800
So why did I use this one?

00:55:46.800 --> 00:55:52.640
I used this one because after
Fukushima, the French Institute

00:55:52.640 --> 00:55:58.920
for Radiation Protection went
to the Fukushima site using

00:55:58.920 --> 00:56:03.160
an energy-resolving
radiation detector,

00:56:03.160 --> 00:56:05.520
like a high purity
germanium detector.

00:56:05.520 --> 00:56:09.680
And they measured the
photon flux off the ground.

00:56:09.680 --> 00:56:14.080
And then they measured the
contamination on the ground,

00:56:14.080 --> 00:56:15.260
and they calculated it.

00:56:15.260 --> 00:56:20.300
And the number that
they got was 0.86.

00:56:20.300 --> 00:56:23.220
It basically
matches this number.

00:56:23.220 --> 00:56:26.160
And that's the most recent
scientific validation of this.

00:56:26.160 --> 00:56:30.560
So I use this number because
it's been validated twice,

00:56:30.560 --> 00:56:32.340
and we know how it was done.

00:56:32.340 --> 00:56:36.980
And the other number that people
have been using for this report

00:56:36.980 --> 00:56:39.740
seems to come out of nowhere.

00:56:39.740 --> 00:56:43.660
Now, here's the caveat.

00:56:43.660 --> 00:56:47.460
That measurement was done four
months after the Fukushima

00:56:47.460 --> 00:56:48.980
accident.

00:56:48.980 --> 00:56:52.500
So it is possible,
in fact, likely,

00:56:52.500 --> 00:56:55.940
that there is a kind
of washing away effect,

00:56:55.940 --> 00:57:00.300
where stuff slowly
settles into the ground

00:57:00.300 --> 00:57:02.700
and becomes less available.

00:57:02.700 --> 00:57:05.500
And therefore, the
dose slowly decays

00:57:05.500 --> 00:57:10.260
from physiochemical
changes in the soil.

00:57:10.260 --> 00:57:14.900
And so we would expect,
actually, some kind of decay

00:57:14.900 --> 00:57:17.060
for this.

00:57:17.060 --> 00:57:20.390
So unfortunately, there
isn't any good studies,

00:57:20.390 --> 00:57:23.870
and it's all extremely
dependent on the soil

00:57:23.870 --> 00:57:26.950
chemistry of where you live.

00:57:26.950 --> 00:57:31.430
But there is one datum taken
six years after the Chernobyl

00:57:31.430 --> 00:57:34.270
accident where they did
this dose estimation.

00:57:34.270 --> 00:57:38.190
And if I take that one datum,
and I fit an exponential decay

00:57:38.190 --> 00:57:41.910
model to it, then
what I would estimate

00:57:41.910 --> 00:57:45.630
is that the cesium
contribution would actually

00:57:45.630 --> 00:57:49.270
be about a fifth of
what we calculated,

00:57:49.270 --> 00:57:54.350
which explains exactly this
differential integrated

00:57:54.350 --> 00:57:55.910
over the lifetime.

00:57:55.910 --> 00:57:59.790
And therefore, if
we go back, and we

00:57:59.790 --> 00:58:02.830
take this number
and this number,

00:58:02.830 --> 00:58:08.890
and we multiply that times a
fifth, you get a smaller value.

00:58:08.890 --> 00:58:10.810
Let's see if I have
it in my notes here.

00:58:27.410 --> 00:58:33.490
Oh, it's about 60% total dose
change, since a lot of this dose

00:58:33.490 --> 00:58:36.530
comes from iodine which
doesn't have that effect.

00:58:36.530 --> 00:58:41.610
So somewhere between
60% of a 230,000.

00:58:41.610 --> 00:58:46.370
And 230,000 is the number that
I think we should go with.

00:58:46.370 --> 00:58:50.230
But that is why there's a lot of
discrepancy in the literature,

00:58:50.230 --> 00:58:56.600
is about how you assume
the dose response would be,

00:58:56.600 --> 00:59:00.510
or the contamination
to dose would be.

00:59:00.510 --> 00:59:03.870
So now let's put some-- let's
convert this into money.

00:59:03.870 --> 00:59:07.650
So we'll have this
in mind that--

00:59:07.650 --> 00:59:09.730
I'll just write it here--

00:59:09.730 --> 00:59:22.375
somewhere between 230,000
and 0.6 times 230,000 deaths.

00:59:22.375 --> 00:59:23.250
I'll use this number.

00:59:23.250 --> 00:59:25.042
And then at the end,
I'll put this back in.

00:59:27.790 --> 00:59:33.190
So how often do these
accidents occur?

00:59:33.190 --> 00:59:38.630
So one of the problems is
that we don't really know.

00:59:38.630 --> 00:59:41.870
And one way that this is
often done is using PRA.

00:59:41.870 --> 00:59:44.785
And I already talked a little
bit about PRA in this class.

00:59:44.785 --> 00:59:47.410
It's a bottom-up approach where
you build these decision trees.

00:59:47.410 --> 00:59:48.910
And then for every
kind of event you

00:59:48.910 --> 00:59:52.670
have to have some probability
that you assign to it.

00:59:52.670 --> 00:59:54.070
And one of the
problems with this

00:59:54.070 --> 00:59:56.810
is that, well, you need
to know a lot of things.

00:59:56.810 --> 00:59:59.750
You need to know every
branching probability.

00:59:59.750 --> 01:00:02.030
And you probably have
never observed most

01:00:02.030 --> 01:00:04.150
of those branches happening.

01:00:04.150 --> 01:00:07.050
And so you're kind of
like guessing at it.

01:00:07.050 --> 01:00:09.910
And it's a little bit of a
garbage in, garbage out model.

01:00:09.910 --> 01:00:11.830
Plus, you have to
decide which trees

01:00:11.830 --> 01:00:13.560
you're going to put on here.

01:00:13.560 --> 01:00:15.120
And one of the
problems is that a lot

01:00:15.120 --> 01:00:20.240
of historical big
accidents have followed

01:00:20.240 --> 01:00:23.255
paths that were not in
the PRA model at the time

01:00:23.255 --> 01:00:24.380
that the accident occurred.

01:00:24.380 --> 01:00:30.560
So we don't really have a priori
belief that the PRA is complete.

01:00:30.560 --> 01:00:34.170
They call this-- so one of
these is-- they call that model

01:00:34.170 --> 01:00:35.920
uncertainty, and they
call the uncertainty

01:00:35.920 --> 01:00:39.020
with all these branching
points, epistemic uncertainty.

01:00:39.020 --> 01:00:42.320
And there's a lot of
uncertainty in these models.

01:00:42.320 --> 01:00:45.520
Nevertheless, the
practitioners of PRA--

01:00:45.520 --> 01:00:47.760
well, the careful
practitioners of PRA

01:00:47.760 --> 01:00:50.760
would never say that you
should take a PRA model

01:00:50.760 --> 01:00:52.400
and take the final
result and use it

01:00:52.400 --> 01:00:57.020
as a measure of the
safety of a reactor.

01:00:57.020 --> 01:00:58.960
All they will say
is, well, if I change

01:00:58.960 --> 01:01:00.880
this thing versus changing
that thing, what is

01:01:00.880 --> 01:01:03.000
my relative change in safety?

01:01:03.000 --> 01:01:05.960
And that's a totally
valid and good use of PRA.

01:01:05.960 --> 01:01:09.960
But there's unfortunately
this temptation

01:01:09.960 --> 01:01:14.520
to take the final number and
treat it as a true number.

01:01:14.520 --> 01:01:21.780
And the NRC has recently adopted
this view when they do back fit.

01:01:21.780 --> 01:01:24.580
And it makes sense for back
fit, because maybe you're

01:01:24.580 --> 01:01:26.760
looking at things which are
explicitly in the model,

01:01:26.760 --> 01:01:28.060
and you're looking
about, how am I

01:01:28.060 --> 01:01:29.643
going to change some
piece of hardware

01:01:29.643 --> 01:01:30.960
to change this value here?

01:01:30.960 --> 01:01:34.380
So you can justify the
use of PRA back fit

01:01:34.380 --> 01:01:37.620
from the perspective of
relative safety change.

01:01:37.620 --> 01:01:39.540
But you can't if
you're going to do

01:01:39.540 --> 01:01:42.660
a cost-benefit
analysis, which then

01:01:42.660 --> 01:01:46.100
assumes a certain
absolute accident risk.

01:01:46.100 --> 01:01:49.460
That's the problem.

01:01:49.460 --> 01:01:52.640
And we have now this discussion
of risk-informed licensing,

01:01:52.640 --> 01:01:56.220
where this is what people want
to do is take this approach

01:01:56.220 --> 01:01:58.580
and assume it to be the
true measure of safety

01:01:58.580 --> 01:01:59.720
of an accident.

01:01:59.720 --> 01:02:05.460
And that's not a good choice
because essentially, we

01:02:05.460 --> 01:02:07.580
are favoring a
model that we know

01:02:07.580 --> 01:02:11.030
to be a, a model, b,
incomplete, and c,

01:02:11.030 --> 01:02:14.630
full of inputs which we
are highly uncertain of,

01:02:14.630 --> 01:02:19.070
in favor of empirical data.

01:02:19.070 --> 01:02:21.350
In Occam's razor,
which we talk about,

01:02:21.350 --> 01:02:24.310
would say any time you have
a model with enormous numbers

01:02:24.310 --> 01:02:27.790
of inputs, you should
be biased against it

01:02:27.790 --> 01:02:34.670
because it's probably missing
something or leading you astray.

01:02:34.670 --> 01:02:37.870
Let's look at the results
produced by these models.

01:02:37.870 --> 01:02:39.810
So here's the core
damage frequency,

01:02:39.810 --> 01:02:42.090
and this is the large,
early release frequency.

01:02:42.090 --> 01:02:45.350
This is the closest thing we
have to a big nuclear reactor

01:02:45.350 --> 01:02:46.270
accident.

01:02:46.270 --> 01:02:50.790
And these are for results for
AP 1,000, the EPR in Europe.

01:02:50.790 --> 01:02:53.490
There's the Chinese-- I'm going
to put a Gen 4 reactor in there.

01:02:53.490 --> 01:02:55.448
This is HTPM from China.

01:02:55.448 --> 01:02:56.990
And then here's the
models for these.

01:02:56.990 --> 01:02:58.810
These are not really
widely published.

01:02:58.810 --> 01:03:01.610
You have to talk to people to
get these numbers-- operating

01:03:01.610 --> 01:03:04.746
VWRs and PWRs.

01:03:04.746 --> 01:03:07.890
And so you can see
what the results are.

01:03:07.890 --> 01:03:10.390
EPR, I think they're
really doing a good job.

01:03:10.390 --> 01:03:13.250
They're basically
just saying, we

01:03:13.250 --> 01:03:16.590
don't really know-- something
less than 10 to the minus 6.

01:03:16.590 --> 01:03:19.970
Incidentally, EPR has a lot of
fancy safety systems compared

01:03:19.970 --> 01:03:23.590
to AP-1000, but it's
much more expensive.

01:03:23.590 --> 01:03:25.450
But AP-1000 people--
Westinghouse

01:03:25.450 --> 01:03:27.450
is willing to put two
digits of significance

01:03:27.450 --> 01:03:31.730
and claim this enormous
exponent of safety.

01:03:31.730 --> 01:03:35.350
And I think that this is
a pretty dubious claim.

01:03:35.350 --> 01:03:37.470
I think EPR people are
doing better at it.

01:03:40.330 --> 01:03:44.790
So if you believe these numbers
are the true measure of safety--

01:03:44.790 --> 01:03:45.410
yep?

01:03:45.410 --> 01:03:46.827
AUDIENCE: I may
have miscaught it.

01:03:46.827 --> 01:03:49.170
What's the unit frequency,
from what to what?

01:03:49.170 --> 01:03:51.490
R. SCOTT KEMP: These
are events per year.

01:03:51.490 --> 01:03:52.350
AUDIENCE: Per year.

01:03:52.350 --> 01:03:52.850
Thank you.

01:03:52.850 --> 01:03:53.683
R. SCOTT KEMP: Yeah.

01:03:53.683 --> 01:03:56.070
So 10 to the minus events--
eight events per year.

01:03:59.050 --> 01:04:01.130
So if you assume
this to be correct,

01:04:01.130 --> 01:04:03.330
we would say how
many large releases

01:04:03.330 --> 01:04:05.350
would we get over 50 years?

01:04:05.350 --> 01:04:11.550
Assuming 80% of global
electricity came from nuclear,

01:04:11.550 --> 01:04:15.470
and we have a linear growth
from where we are now

01:04:15.470 --> 01:04:18.910
to get to that in 50 years.

01:04:18.910 --> 01:04:20.850
And so I've done the
integral for you.

01:04:20.850 --> 01:04:23.590
And look, I mean,
basically not zero.

01:04:23.590 --> 01:04:25.150
You would have no
accidents, even

01:04:25.150 --> 01:04:28.830
though 80% of the power in
the world came from nuclear.

01:04:28.830 --> 01:04:31.430
Here is less than 0.4.

01:04:31.430 --> 01:04:34.630
Only for existing
operating BWR would

01:04:34.630 --> 01:04:39.970
you have more than
one accident per year.

01:04:44.070 --> 01:04:47.590
If you're in this regime,
you would have a problem.

01:04:47.590 --> 01:04:50.190
Can you imagine having a
large nuclear reactor accident

01:04:50.190 --> 01:04:51.410
every single year?

01:04:51.410 --> 01:04:54.930
AUDIENCE: [INAUDIBLE] 50 years?

01:04:54.930 --> 01:04:57.100
R. SCOTT KEMP: Oh.

01:04:57.100 --> 01:04:57.600
Yes.

01:05:02.310 --> 01:05:03.410
Yes, you're right.

01:05:03.410 --> 01:05:03.550
Yeah.

01:05:03.550 --> 01:05:04.883
So this would be-- that's right.

01:05:04.883 --> 01:05:06.900
This would be roughly
one every 50 years.

01:05:06.900 --> 01:05:09.520
So that's basically
where we are now.

01:05:09.520 --> 01:05:11.660
So that would be fine.

01:05:11.660 --> 01:05:13.048
That would be fine.

01:05:13.048 --> 01:05:14.840
Well, I don't know
about fine, but that's--

01:05:14.840 --> 01:05:15.960
AUDIENCE: It's not bad.

01:05:15.960 --> 01:05:16.380
R. SCOTT KEMP: It's not bad.

01:05:16.380 --> 01:05:18.297
It's better than what
we've seen historically.

01:05:18.297 --> 01:05:19.600
AUDIENCE: [INAUDIBLE]

01:05:19.600 --> 01:05:21.240
R. SCOTT KEMP: Yeah.

01:05:21.240 --> 01:05:24.040
So this if these
models are correct,

01:05:24.040 --> 01:05:27.240
we really have nothing
to fear from nuclear.

01:05:27.240 --> 01:05:29.720
But the problem is
that the history is not

01:05:29.720 --> 01:05:30.700
comport with that.

01:05:30.700 --> 01:05:34.920
So these are the actual
accidents, different INES

01:05:34.920 --> 01:05:35.420
scales.

01:05:35.420 --> 01:05:36.170
There's Chernobyl.

01:05:36.170 --> 01:05:37.800
There's Fukushima.

01:05:37.800 --> 01:05:40.340
The ones that are not
black, the open circles,

01:05:40.340 --> 01:05:43.730
these are nonreactor
fuel cycle accidents.

01:05:43.730 --> 01:05:45.480
So they are associated
with nuclear power,

01:05:45.480 --> 01:05:47.400
but they are not reactors.

01:05:47.400 --> 01:05:52.360
So this is a Soviet
fuel reprocessing site.

01:05:52.360 --> 01:05:54.760
These are also such sites.

01:05:54.760 --> 01:06:01.320
And you see that they also
can contribute significantly.

01:06:01.320 --> 01:06:03.180
Another thing to see
is that this basically

01:06:03.180 --> 01:06:04.280
kind of like a power law.

01:06:04.280 --> 01:06:09.880
We expect more accidents as
we get to lower intensity;

01:06:09.880 --> 01:06:12.120
fewer accidents as we
get to worse intensity.

01:06:12.120 --> 01:06:14.140
But it's not
exactly a power law.

01:06:14.140 --> 01:06:16.700
There's only one INES 6.

01:06:16.700 --> 01:06:19.080
That's probably because
of quantization noise.

01:06:19.080 --> 01:06:20.522
We're a little
bit undersampling.

01:06:20.522 --> 01:06:21.980
And the other thing
to point out is

01:06:21.980 --> 01:06:26.500
that the accident
rate is decreasing,

01:06:26.500 --> 01:06:30.020
at least for category 4.

01:06:30.020 --> 01:06:31.560
So maybe things
are getting safer.

01:06:31.560 --> 01:06:33.940
I would argue that they
have been getting safer.

01:06:33.940 --> 01:06:36.860
We're better at safety.

01:06:36.860 --> 01:06:42.660
So what should we assume
for these big accidents?

01:06:42.660 --> 01:06:45.100
So here's the thing.

01:06:45.100 --> 01:06:48.780
These large INES 7
accidents are typically

01:06:48.780 --> 01:06:52.780
what we call design beyond
design basis accidents.

01:06:52.780 --> 01:06:57.260
That means we did not do things
to the reactor to prevent

01:06:57.260 --> 01:06:59.180
these accidents from occurring.

01:06:59.180 --> 01:07:02.030
So although we are
improving the reactor safety

01:07:02.030 --> 01:07:06.950
for small events which
we are designing for,

01:07:06.950 --> 01:07:09.750
we are not doing anything
to deal with these

01:07:09.750 --> 01:07:11.985
beyond design basis accidents.

01:07:11.985 --> 01:07:13.110
AUDIENCE: Well, that goes--

01:07:13.110 --> 01:07:14.910
doesn't go for
Chernobyl, though.

01:07:14.910 --> 01:07:19.750
You can't just pull out
all your [INAUDIBLE].

01:07:19.750 --> 01:07:22.427
I get it from Fukushima,
but Chernobyl, I

01:07:22.427 --> 01:07:24.010
feel like it's kind
of the equivalent,

01:07:24.010 --> 01:07:27.430
from an operator standpoint,
of getting blackout wasted,

01:07:27.430 --> 01:07:30.057
driving your car
into an [INAUDIBLE].

01:07:30.057 --> 01:07:30.890
R. SCOTT KEMP: Yeah.

01:07:30.890 --> 01:07:32.050
But that's-- exactly.

01:07:32.050 --> 01:07:34.950
That's why it's beyond
design basis accident.

01:07:34.950 --> 01:07:37.650
It's like the operator
did something stupid.

01:07:37.650 --> 01:07:40.870
And there's nothing to say that
some operator of the future

01:07:40.870 --> 01:07:43.230
won't also do something stupid.

01:07:46.340 --> 01:07:49.310
There's going to be all kinds
of these things that haven't

01:07:49.310 --> 01:07:51.070
happened that you can imagine--

01:07:51.070 --> 01:07:55.910
terrorist attacks,
whatever-- that could

01:07:55.910 --> 01:07:59.690
result in intentional sabotage.

01:07:59.690 --> 01:08:02.770
So there are going
to be these events,

01:08:02.770 --> 01:08:07.330
and it's going to be really hard
to know what their frequency is.

01:08:07.330 --> 01:08:12.850
What I suggest is that in the
absence of any good guidance

01:08:12.850 --> 01:08:16.770
about how often these
things will occur,

01:08:16.770 --> 01:08:19.210
the best, most defensible
thing we can do

01:08:19.210 --> 01:08:23.010
is just take the
historical rate and say,

01:08:23.010 --> 01:08:30.050
that's what we've seen for these
beyond design basis accidents.

01:08:30.050 --> 01:08:33.390
Anything else, you're injecting
some additional information.

01:08:33.390 --> 01:08:38.170
And I don't know that we have
any additional information.

01:08:38.170 --> 01:08:41.450
So here's the
history of reactor.

01:08:41.450 --> 01:08:45.250
We have 21,500 reactor
years of experience,

01:08:45.250 --> 01:08:50.930
and expectation over 50 years
with no growth would be about

01:08:50.930 --> 01:08:55.472
two reactor accidents, which
is kind of what we've seen.

01:08:55.472 --> 01:08:56.930
But if we did--
again, here's where

01:08:56.930 --> 01:08:58.689
I was going to make
that point earlier.

01:08:58.689 --> 01:09:01.710
If we did have that
growth to 80% electricity,

01:09:01.710 --> 01:09:06.990
we would be at 40 INES 7
events every 50 years, which

01:09:06.990 --> 01:09:09.590
would be roughly one
per year, and then we

01:09:09.590 --> 01:09:12.350
would have a problem.

01:09:12.350 --> 01:09:16.290
So this is the problem
with these events--

01:09:16.290 --> 01:09:18.710
a major global expansion
of nuclear power.

01:09:18.710 --> 01:09:23.350
Unless this beyond design basis
number somehow comes down,

01:09:23.350 --> 01:09:25.910
it still presents
an ongoing problem

01:09:25.910 --> 01:09:28.390
that we have to deal
with that would basically

01:09:28.390 --> 01:09:30.410
kill the public
acceptance of nuclear,

01:09:30.410 --> 01:09:35.130
I would argue, at roughly
an accident a year--

01:09:35.130 --> 01:09:37.670
giant accident a year.

01:09:37.670 --> 01:09:38.283
Yeah?

01:09:38.283 --> 01:09:39.950
AUDIENCE: Could we
also argue that if we

01:09:39.950 --> 01:09:41.950
saw an increase in these
types of accidents that

01:09:41.950 --> 01:09:44.590
were, like you were
saying, beyond design

01:09:44.590 --> 01:09:48.229
basis, human error, and we
start-- if we have those more

01:09:48.229 --> 01:09:51.710
often, would we not
then be, I guess,

01:09:51.710 --> 01:09:55.948
incentivized to make that
more safe more quickly.

01:09:55.948 --> 01:09:57.240
R. SCOTT KEMP: I would hope so.

01:09:57.240 --> 01:09:59.400
So we would have thought
that after Fukushima, we

01:09:59.400 --> 01:10:00.940
would have made--

01:10:00.940 --> 01:10:04.520
we would have added filter
vents, and most of the world

01:10:04.520 --> 01:10:05.020
did.

01:10:05.020 --> 01:10:07.560
But the United States said no.

01:10:07.560 --> 01:10:09.307
So it depends.

01:10:09.307 --> 01:10:11.640
If it's happening every year,
I think political pressure

01:10:11.640 --> 01:10:14.363
to do it would be a lot more.

01:10:14.363 --> 01:10:15.280
AUDIENCE: [INAUDIBLE].

01:10:15.280 --> 01:10:17.960
I guess-- I hope we did learn
not to site them in places that

01:10:17.960 --> 01:10:20.125
historically have tsunamis.

01:10:20.125 --> 01:10:21.500
R. SCOTT KEMP:
Hopefully, we did.

01:10:21.500 --> 01:10:25.960
We'll find out.

01:10:25.960 --> 01:10:27.682
AUDIENCE: Probably not.

01:10:27.682 --> 01:10:29.140
R. SCOTT KEMP: This
is the problem.

01:10:29.140 --> 01:10:30.820
I think memory is short.

01:10:30.820 --> 01:10:33.840
It's like there's some half
life associated with learning

01:10:33.840 --> 01:10:35.680
from these events.

01:10:35.680 --> 01:10:38.180
In the immediate
aftermath of Fukushima,

01:10:38.180 --> 01:10:39.780
everyone is angry at nuclear.

01:10:39.780 --> 01:10:40.580
Everyone hates it.

01:10:40.580 --> 01:10:42.420
Enrollments in nuclear
engineering drop.

01:10:42.420 --> 01:10:46.800
And then three years later,
everything creeps back up

01:10:46.800 --> 01:10:49.080
and people forget.

01:10:49.080 --> 01:10:50.980
So we'll see.

01:10:50.980 --> 01:10:52.880
So we can just
take these numbers,

01:10:52.880 --> 01:10:59.540
and we can calculate a large
early release frequency.

01:10:59.540 --> 01:11:01.980
I guess you can't really
see that this is red.

01:11:01.980 --> 01:11:07.420
So if we take that rate, and
we take the existing fleet,

01:11:07.420 --> 01:11:10.820
and we take the
weighted average,

01:11:10.820 --> 01:11:14.080
we would see that we
would be at 4-- sorry.

01:11:14.080 --> 01:11:17.380
This is the PRA result. We
are at 2 times to the minus 4.

01:11:17.380 --> 01:11:19.780
The PRA result for
the existing fleet

01:11:19.780 --> 01:11:22.740
says we should be at 4.5
times 10 to the minus 6.

01:11:22.740 --> 01:11:26.780
This is the evidence that
the PRA result is incomplete.

01:11:26.780 --> 01:11:29.620
PRA has said the
reactors operating

01:11:29.620 --> 01:11:33.380
today had this accident
rate, and this is the rate

01:11:33.380 --> 01:11:35.840
that we've actually observed.

01:11:35.840 --> 01:11:41.180
It's a factor of 50
times difference.

01:11:41.180 --> 01:11:45.580
So the PRA is only
capturing a small fraction

01:11:45.580 --> 01:11:47.920
of the total risk.

01:11:47.920 --> 01:11:50.740
Let me see if I can blast
through and finish this up.

01:11:50.740 --> 01:11:55.900
So here, we can pick-- various
is the NRC safety target.

01:11:55.900 --> 01:11:59.200
Here's a historical accident
rate for all events over 5

01:11:59.200 --> 01:12:01.340
to match the safety target.

01:12:01.340 --> 01:12:05.000
Here's the true historical
rate for only INES 7.

01:12:05.000 --> 01:12:06.860
If you go back and
look at this plot--

01:12:09.840 --> 01:12:13.880
if you look at these other
events, pretty tiny releases--

01:12:13.880 --> 01:12:18.880
0.2 petabecquerel, 0.013
petabecquerel cesium--

01:12:18.880 --> 01:12:19.960
tiny.

01:12:19.960 --> 01:12:23.380
Only these big things
beyond design basis matter.

01:12:23.380 --> 01:12:25.440
So my suggestion
is we just ignore

01:12:25.440 --> 01:12:26.620
all these other accidents.

01:12:26.620 --> 01:12:27.720
They don't matter.

01:12:27.720 --> 01:12:31.240
Only things that matter are the
beyond design basis accidents.

01:12:31.240 --> 01:12:37.600
And so we'll take only the
beyond design the INES 7 rate

01:12:37.600 --> 01:12:40.660
as our accident rate, and
we'll ignore all these others.

01:12:40.660 --> 01:12:44.080
And that is 10 to the
minus 4 per reactor year.

01:12:44.080 --> 01:12:47.280
And if we assume that every
reactor is roughly a gigawatt,

01:12:47.280 --> 01:12:52.370
it's 10 to the minus
11 per megawatt hour.

01:12:52.370 --> 01:12:55.070
And then we can take
our number of deaths--

01:12:57.670 --> 01:13:03.610
so 10-- we want
terawatt hours, which

01:13:03.610 --> 01:13:07.010
is 10 to the 12 watt hours.

01:13:07.010 --> 01:13:13.650
And that is equal to 10
to the 6 megawatt hours.

01:13:13.650 --> 01:13:19.050
And we had, from the previous
slide, 10 to the minus 11

01:13:19.050 --> 01:13:20.450
per megawatt hour.

01:13:20.450 --> 01:13:32.600
So the accident rate is 10
to the minus 11 accidents

01:13:32.600 --> 01:13:37.730
per megawatt hour times
10 to the 6 megawatt

01:13:37.730 --> 01:13:42.250
hours per terawatt hour.

01:13:42.250 --> 01:13:44.370
And that gives us--

01:13:44.370 --> 01:13:45.090
what is it?

01:13:48.830 --> 01:13:51.390
10 to the minus 5?

01:13:51.390 --> 01:13:54.570
10 to the minus 5 accidents
per terawatt hour.

01:14:01.950 --> 01:14:13.150
And 10 to the minus 5 accidents
times 230,000 deaths per

01:14:13.150 --> 01:14:20.770
accident is equal to 2.3
deaths per terawatt hour.

01:14:24.430 --> 01:14:28.050
So now we can put our
number on the chart.

01:14:28.050 --> 01:14:29.510
There it is--

01:14:29.510 --> 01:14:32.510
2.3 deaths per terawatt hour.

01:14:32.510 --> 01:14:36.110
And if we assume the washing
away effect of the cesium,

01:14:36.110 --> 01:14:38.990
it goes down all the way to 1.4.

01:14:38.990 --> 01:14:40.450
So is nuclear safe?

01:14:40.450 --> 01:14:42.070
Yes.

01:14:42.070 --> 01:14:45.190
Nuclear is a pretty
safe form of energy.

01:14:45.190 --> 01:14:50.160
It's not as safe as
they said it was.

01:14:50.160 --> 01:14:52.000
It's a lot worse than that.

01:14:52.000 --> 01:14:57.520
But it's somewhere between
hydro and natural gas.

01:14:57.520 --> 01:14:59.160
It's relatively safe.

01:14:59.160 --> 01:14:59.680
Yeah?

01:14:59.680 --> 01:15:01.100
AUDIENCE: [INAUDIBLE]
the other--

01:15:01.100 --> 01:15:03.800
if they got nuclear
wrong, what [INAUDIBLE]?

01:15:03.800 --> 01:15:05.340
R. SCOTT KEMP: Oh, thank you.

01:15:05.340 --> 01:15:05.840
Yeah.

01:15:05.840 --> 01:15:09.640
We really shouldn't trust
anything on this chart now.

01:15:09.640 --> 01:15:14.240
So what we're going to do,
maybe in the next class,

01:15:14.240 --> 01:15:15.840
is we'll look at
other calculations

01:15:15.840 --> 01:15:17.300
for these other factors.

01:15:17.300 --> 01:15:17.800
Yeah.

01:15:20.600 --> 01:15:22.920
And why don't I stop there.

01:15:22.920 --> 01:15:24.470
Yeah.

