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ENVIRONMENT |
han a constant-velocity wind

the measurementstations, and dot

beginning of spill 1. The crosses in-

The ATMAScode models atmospheric transport by solving the
advection-diffusion equation,
which simply states that the con-

tions. Figure 2 shows a contour plot
of the concentration isopleths 1 m
above the ground 60s after the

this experiment, the wind carried

model.

plots of marker-particle distribu-

centration of pollutants at a given

400

point is determined by two

I

dicate the measurementstations.In

muchof the plume to theleft of the
detector array.

|

|

processes: diffusion (the simple

spreading that takes place without
wind and the effects of gusts and

eddies) and advection (blowing
away in the average wind). ATMAS

uses the particle-in-cell method,°
which represents the mass of the
emitted pollutant by marker particles whose trajectories through
space are calculated according to
_an equation of motion derived
from the advection-diffusion equation. The array of marker particles
gives us a graphic threedimensional representation of the
vapor plume.
To use the ATMAScode, we
must specify boundary conditions,
the characteristics of the LNG
vapor source, and measuredvalues
of wind speed and direction as a
function of time. Forthe first three
experiments we assumed a constant emission rate from a round
LNG pool of constant size for a
fixed period of time. In the fourth

0.585 g/m®

300 + |

~

E
i

8 200 -

—

a

2

—

100 }-

29.2 g/m?

test, because of significant changes

87.7 g/m"

in wind velocity, we found it
necessary to simulate the way in
which the LNG pool spreads over

175 g/m?
0

the water surface. We did this by

turning on a series of vapor sources
with successively larger areas from
time to time during the calculation.
The various 5-m* tests are
described in Table 1.
The ATMAScode displays the

x

0

i

.

50

D

|

100
Distance — m

|

150

;

200

Concentration isopleths calculated by the

Oi,
ATMAScode for the vapor plume 60 s
after the start of thefirst 5-m’ spill experiment. The lower

flammability limit (33 g/m? at 300 K) eventually extended to about 380 m.

results of its calculations in contour

plots of gas concentration, graphs
of concentration vs time for each of

31

Select target paragraph3