1
UNITED
STATES
ENVIRONMENTAL
PROTECTION
AGENCY
WASHINGTON,
D.
C.
20460
OFFICE
OF
PESTICIDE
PROGRAMS,

PC
Code:
129016
DPBarcode:
301361
May
19,
2004
MEMORANDUM
SUBJECT:
Drinking
Water
Assessment
for
Flumetsulam
for
Uses
on
Field
Corn
and
Soybeans
FROM:
James
Lin,
Environmental
Engineer
Stephanie
Syslo,
RAPL
Environmental
Risk
Branch
III
Environmental
Fate
and
Effects
Division
(
7507C)

THRU:
Ben
Smith,
Branch
Chief
Environmental
Risk
Branch
III
Environmental
Fate
and
Effects
Division
(
7507C)

TO:
Diana
Locke
Health
and
Effects
Division
(
7509C)
and
Daniel
Helfgott
Special
Review
and
Reregistration
Division
(
7508C)

This
memo
provides
the
estimated
drinking
water
concentrations
from
surface
water
and
ground
water
sources
for
assisting
Health
and
Effects
Division
in
determining
the
potential
risk
to
human
health.
The
drinking
water
assessment
is
based
solely
on
model­
estimated
exposure
concentrations
in
surface
water
and
ground
water.

Flumetsulam
is
a
selective
herbicide
for
use
to
control
broadleaf
weeds
in
soybeans
and
field
corn.
It
belongs
to
the
triazolopyrimidine
chemical
family.
The
physical
chemical
properties
of
flumetsulam
are
included
as
Attachment
1.
The
mode
of
action
is
similar
to
the
sulfonylurea
herbicides,
which
are
ALS
(
Acetolactate
synthase)
inhibitors.
Flumetsulam
can
be
applied
alone,
such
as
in
Python
®
or
Broadstrike
®
,
or
applied
in
formulation
with
other
active
ingredients,
such
as
in
Hornet
®
(
flumetsulam
+
clopyralid),
Accent
Gold
®
(
flumetsulam
+
clopyralid
+
2
Nicosulfuron),
Broadstrike
+
Dual
®
(
flumetsulam
+
metolachlor),
Broadstrike
+
Treflan
®
(
flumetsulam
+
trifluralin)
and
others.
Since
only
flumetsulam
will
be
considered
in
this
drinking
water
assessment,
the
maximum
allowable
application
rate
for
flumetsulam
alone
of
0.07
lb
a.
i./
acre
will
be
used
to
simulate
corn
and
soybeans
uses
.
Both
aerial
and
ground
application
are
allowed
in
the
labels.
The
exposure
concentrations
of
drinking
water
were
estimated
for
aerial
applications,
as
drift
from
aerial
applications
result
in
higher
exposure
concentrations
in
surface
water
than
ground
applications.

The
estimated
drinking
water
concentrations
of
flumetsulam
in
surface
water
are
summarized
in
Table
1.
Among
EFED's
standard
crop
scenarios,
there
are
nine
scenarios
for
corn
and
only
one
for
soybeans.
The
Mississippi
corn
scenario
predicts
the
highest
1­
in­
10
year
peak
concentrations
of
2.03

g/
L,
whereas
the
North
Dakota
corn
scenario
gives
the
highest
1­
in­
10
annual
mean
of
0.59

g/
L,
and
overall
annual
mean
of
0.34

/
L.
Table
2
summarizes
the
estimated
drinking
water
concentrations
of
flumetsulam
in
ground
water.
Both
acute
and
chronic
estimates
are
0.823

g/
L.

Table
1.
Estimated
Drinking
Water
Concentrations
of
Flumetsulam
from
Surface
Water
Sources.
Simulation
based
on
aerial
application
and
the
water
values
are
adjusted
with
percent
crop
area
factor
(
0.46
for
corn
and
0.41
for
soybeans).
Concentrations
are
in

g/
L
(
ppb)

Agricultural
Commodity/
State
1­
in­
10
yr
Peak
1­
in­
10
yr
Annual
Mean
Overall
Annual
Mean
Value
Corn
/
California
0.59
0.34
0.19
Corn
/
Illinois
1.01
0.30
0.22
Corn
/
Mississippi
2.03
0.46
0.23
Corn
/
East
North
Carolina
0.96
0.30
0.16
Corn
/
West
North
Carolina
0.90
0.23
0.12
Corn
/
North
Dakota
1.22
0.59
0.34
Corn
/
Ohio
0.85
0.29
0.17
Corn
/
Pennsylvania
1.15
0.48
0.28
Corn
/
Texas
1.16
0.28
0.13
Soybeans
/
Mississippi
1.03
0.22
0.14
3
Table
2.
Estimated
Drinking
Water
Concentrations
of
Flumetsulam
from
Ground
Water
Sources.
Concentrations
are
in

g/
L
(
ppb)

Acute
0.823
Chronic
0.823
Models,
Scenarios,
and
Input
Parameters
Used
Estimate
Concentrations
of
Flumetsulam
The
estimated
drinking
water
concentrations
from
surface
water
sources
were
calculated
using
Tier
II
PRZM
(
Pesticide
Root
Zone
Model)
and
EXAMS
(
Exposure
Analysis
Modeling
System).
PRZM
is
used
to
simulate
pesticide
transport
as
a
result
of
runoff
and
erosion
from
an
agricultural
field
and
EXAMS
estimates
environmental
fate
and
transport
of
pesticides
in
surface
water
and
using
the
linkage
program
shell
­
PE4v01
(
dated
08/
13/
2003),
which
incorporates
the
standard
scenarios
developed
by
EFED.

Linked
crop­
specific
scenarios
and
meteorological
data
were
used
to
estimate
exposure
as
a
result
of
uses
on
field
corn
and
soybeans.
Simulations
were
done
using
the
Index
Reservoir
scenario
in
EXAMS,
which
is
a
surrogate
for
a
drinking
water
source
drawn
from
surface
water.
Weather
and
agricultural
practices
are
simulated
over
30
years
so
that
the
1­
in10
year
exceedence
probability
at
the
site
can
be
estimated.
The
values
generated
by
the
models
for
drinking
water
were
multiplied
by
a
crop
area
factor
(
PCA),
which
accounts
for
the
fact
that
it
is
unlikely
for
any
basin
to
be
completely
planted
to
an
agricultural
crop.
The
maximum
PCA
for
corn
is
0.46
and
the
value
for
soybeans
is
0.41.

Concentrations
in
ground
water
were
estimated
using
the
Tier
I
SCI­
GROW
(
Screening
Concentration
In
Ground
Water)
model.

For
further
information
on
these
models
see,

http://
www.
epa.
gov/
oppefed1/
models/
water/
index.
htm
Surface
water
Nine
standard
scenarios
for
corn
and
one
for
soybeans
were
simulated
for
this
drinking
water
assessment.
These
scenarios
are
briefly
identified
in
Table
3.
Since
flumetsulam
applications
are
simulated
as
pre­
plant
application,
the
scenario
specific
pre­
planting
dates
are
also
included
in
Table
3.
4
Table
3.
Scenarios
Used
to
Estimate
Drinking
Water
Concentrations
of
Flumetsulam
from
Surface
Water
Sources
CA
­
Corn
MLRA
17,
Stanislaus/
San
Joaquin
Counties,
Metfile:
W23232.
dvf,
Soil:
Madera
Loam
Pre­
planting
Date:
3/
24
IL
­
Corn
MLRA
108,
Mclean
County,
Metfile:
W14923.
dvf,
Soil:
Adair
Clay
Loam
Pre­
planting
Date:
4/
17
MS
­
Corn
MLRA
134,
Southern
MS
Valley
Upland,
Metfile:
W13893.
dvf,
Soil:
Grenada
Silt
Loam
Pre­
planting
Date:
3/
28
NC
(
east)
­
Corn
MLRA
133,
Pitt
County,
Metfile:
W13722.
dvf,
Soil:
Craven
Silt
Loam
Pre­
planting
Date:
3/
28
NC
(
west)
­
Corn
MLRA
130,
Henderson
County,
Metfile:
W03812.
dvf,
Soil:
Chewacla
Loam
Pre­
planting
Date
4/
11:

ND
­
Corn
MLRA
56,
Red
River
Valley,
Pembina
County,
Metfile:
W14914.
dvf,
Soil:
Bearden
Silty
Clay
Loam
Pre­
planting
Date:
4/
20
OH
­
Corn
MLRA
111,
Darke
and
Rickaway
Counties,
Metfile:
W93815.
dvf,
Soil:
Cardington
Silt
Loam
Pre­
planting
Date:
4/
16
PA
­
Corn
MLRA
148,
Lancaster
County,
Metfile:
W14737.
dvf,
Soil:
Hagerstown
Silt
Loam
Pre­
planting
Date:
4/
05
TX
­
Corn
MLRA
87,
Texas
Claypan
Area,
Milam
County,
Metfile:
W13958.
dvf,
Soil:
Axtell
Sandy
Loam
Pre­
planting
Date:
2/
24
MS
­
Soybeans
MRLA
134,
Yazoo
County,
Metfile:
W13893,
Soil:
Loring
Silt
Loam
Pre­
planting
Date:
3/
31
Ground
Water
SCI­
GROW
is
a
regression
model,
which
is
not
designed
for
specific
scenario
or
specific
crop.

Input
Parameters
The
appropriate
PRZM,
EXAMS,
and
SCI­
GROW
input
parameters
were
selected
from
the
environmental
fate
data
submitted
by
the
petitioner
and
in
accordance
with
US
EPA­
OPP
EFED
water
model
parameter
selection
guidelines,
Guidance
for
Selecting
Input
Parameters
in
Modeling
the
Environmental
Fate
and
Transport
of
Pesticides,
Version
II,
February
28,
2002.

Attachment
2
presents
the
input
parameters
used
in
the
PRZM,
EXAMS,
and
SCI­
GROW
5
models.

Outputs
The
output
files
of
CA
corn
and
MS
soybeans
are
included
in
Attachment
3.
6
Attachment
1:
Product
Chemistry
of
Flumetsulam
Molecular
Formula:
C
12
H
9
F
2
N
5
O
2
S
Molecular
Weight:
325.3
Molecular
Structure:

Water
Solubility:
5650
mg/
L
@
pH
7.0
(
25
oC)
49.1
mg/
L
@
pH
2.5
(
25
oC)

Vapor
Pressure:
0.8
x
10­
15
mmHg
(
20
oC)

log
Kow:
0.21
@
pH
7
pKa:
4.6
7
Attachment
2:
Input
values
of
PRZM,
EXAMS,
and
SCIGROW
Table
2­
1.
Input
Parameters
for
PRZM
with
Flumetsulam
(
version
3.12,
dated
05/
07/
1998)

Variable
(
units)
Variable
Description
Input
Value
Source
of
Info/
Reference
DWRATE(
1)
1
(
day­
1)
Dissolved
phase
pesticide
decay
rate
in
surface
horizon
DWRATE(
1)
=
DSRATE(
1)

The
90th
percentile
half­
life
value
of
98.9
days
Aerobic
soil
metabolism
half­
life
values
of
23,
60,
93,
and
102
days
DSRATE(
1)
1
(
day­
1)
Adsorbed
phase
pesticide
decay
rate
in
surface
horizon
DWRATE(
2)
(
day­
1)
DWRATE(
3)
(
day­
1)
Dissolved
phase
pesticide
decay
rate
in
1st,
and
2nd
subsurface
horizon
DWRATE(
2)
=
DSRATE(
2)

The
90th
percentile
half­
life
value
of
98.9
days
DWRATE(
3)
=
DSRATE(
3)

The
90th
percentile
half­
life
value
of
98.9
days
same
as
above
DSRATE(
2)
(
day­
1)
DSRATE(
3)
(
day­
1)
Adsorbed
phase
pesticide
decay
rate
in
1st
and
2nd
subsurface
horizon
KD(
1)
KD(
2)
KD(
3)
(
cm3
gm­
1
or
mL
g­
1
or
L
kg­
1)
Pesticide
partition
or
distribution
coefficients
for
each
horizon
assume
a
mean
KOC
of
27.23
Mobility
­
Adsorption/
Desorption
study
(
GLN
163­
1)
42,
24,
21,
5,
31,
18,
32,
71,
13,
47,
24,
10,
21,
74,
13,
10,
17,
10,
38,
39,
24,
15
PLDKRT
(
day­
1)
Foliar
decay
rate
not
used,
since
pre­
plant
application
were
simulated
TAPP
(
kg
ha­
1)
Application
rate
0.07
lb
a.
i./
ac
Product
label
APPEFF
(
decimal)
Application
efficiency
0.95
for
aerial
spray
input
guidance
document
DRFT
Spray
drift
fraction
0.16
for
aerial
spray
for
index
reservoir
input
guidance
document
8
Table
2­
2.
Input
Parameters
for
EXAMS
with
Flumetsulam
(
version
2.98,
dated
07/
18/
2002)

Variable
(
units)
Variable
Description
Input
Value
Source
of
Info/
Reference
HENRY
(
atm­
m3mole­
1)
Henry's
law
constant
no
input,
let
EXAMS
computes
KBACW1
(
cfu/
mL)­
1
hour­
1
Bacterial
biolysis
in
water
column
2
x
98.8
days
2x
of
soil
aerobic
metabolism
half­
life
KBACS1
(
cfu/
mL)­
1
hour­
1
Bacterial
biolysis
in
benthic
sediment
183
days
input
as
the
half­
life
aquatic
anaerobic
halflife
of
183
days
KDP
(
hour­
1)
Direct
photolysis
0.0
stable
KBH
(
mole­
1
hour­
1)
KNH
(
hour­
1)
KAH
(
mole­
1
hour­
1)
Base
hydrolysis
Neutral
hydrolysis
Acid
hydrolysis
0.0
0.0
0.0
stable
KOC
(
mL
g­
1
O.
C.)
Partition
coefficient
for
organic
carbon
27.23
average
value
MWT
(
g
mole­
1)
Molecular
weight
325.3
product
chemistry
SOL
(
mg
L­
1)
Aqueous
solubility
5650
product
chemistry
QUANT
Reaction
quantum
yield
for
direct
photolysis
1.0
VAPR
(
torr)
Vapor
pressure
0.8
x
10­
15
product
chemistry
9
Table
2­
3.
Input
Parameters
for
SCIGROW
(
version
2.3,
dated
07/
29/
2003)

Variable
Description
Input
Value
Soil
half­
life
(
day)
mean
value
of
69.5
days
(
23,
60,
93,
and
102
days)

Pesticide
partition
or
distribution
coefficients,
Koc
5
(
greater
than
a
three­
fold
variation
in
all
values:
42,
24,
21,
5,
31,
18,
32,
71,
13,
47,
24,
10,
21,
74,
13,
10,
17,
10,
38,
39,
24,
15)

Application
rate
0.07
lb
a.
i./
ac
10
Attachment
3
Output
files
(
only
CA
corn
and
MS
soybeans
are
attached)

stored
as
CAcornF.
out
Chemical:
Flumetsulam
PRZM
environment:
CAcornC.
txt
modified
Satday,
12
October
2002
at
16:
32:
58
EXAMS
environment:
ir298.
exv
modified
Thuday,
29
August
2002
at
15:
34:
12
Metfile:
w23232.
dvf
modified
Wedday,
3
July
2002
at
09:
04:
22
Water
segment
concentrations
(
ppb)

Year
Peak
96
hr
21
Day
60
Day
90
Day
Yearly
1961
0.4578
0.4529
0.436
0.4001
0.3741
0.189
1962
0.5462
0.5418
0.5225
0.4794
0.4486
0.285
1963
4.089
4.056
3.919
3.625
3.398
1.797
1964
1.29
1.28
1.237
1.141
1.071
0.7738
1965
0.7561
0.7498
0.7327
0.6825
0.6411
0.4028
1966
0.6175
0.6124
0.5901
0.5405
0.5049
0.3028
1967
0.8766
0.8697
0.8443
0.7915
0.7428
0.4186
1968
0.6342
0.6289
0.6064
0.557
0.521
0.3135
1969
1.164
1.154
1.113
1.02
0.9516
0.5264
1970
0.6919
0.6861
0.6621
0.6096
0.5696
0.3532
1971
0.8215
0.8148
0.7862
0.7263
0.6817
0.3866
1972
0.6214
0.6159
0.5935
0.5454
0.5098
0.3042
1973
0.5813
0.5766
0.5561
0.5094
0.4746
0.2732
1974
0.5696
0.5648
0.5455
0.5024
0.4707
0.2722
1975
0.5725
0.568
0.549
0.5068
0.4736
0.2696
1976
0.587
0.5819
0.5609
0.5366
0.5047
0.2867
1977
0.5778
0.5731
0.5527
0.5154
0.4875
0.286
1978
0.5769
0.5719
0.5601
0.5239
0.4911
0.284
1979
0.9037
0.896
0.8639
0.7934
0.7405
0.411
1980
0.7691
0.7629
0.7384
0.6806
0.6387
0.3778
1981
0.7075
0.7018
0.6772
0.6266
0.5869
0.3414
1982
0.7302
0.7241
0.7027
0.6494
0.6121
0.3582
1983
0.6148
0.6097
0.5887
0.5449
0.5111
0.3031
1984
0.5752
0.5701
0.5519
0.5068
0.4722
0.2691
1985
0.6113
0.6064
0.5848
0.5387
0.5039
0.2858
1986
0.6485
0.6428
0.6192
0.5792
0.5482
0.3171
1987
0.5934
0.5884
0.5669
0.5183
0.4829
0.2912
1988
0.8583
0.8505
0.8206
0.7491
0.6953
0.4112
1989
2.174
2.155
2.076
1.901
1.774
0.9552
1990
0.8833
0.8761
0.8445
0.7743
0.7313
0.4893
Sorted
results
Prob.
Peak
96
hr
21
Day
60
Day
90
Day
Yearly
0.032258064516129
4.089
4.056
3.919
3.625
3.398
1.797
0.0645161290322581
2.174
2.155
2.076
1.901
1.774
0.9552
0.0967741935483871
1.29
1.28
1.237
1.141
1.071
0.7738
0.129032258064516
1.164
1.154
1.113
1.02
0.9516
0.5264
0.161290322580645
0.9037
0.896
0.8639
0.7934
0.7428
0.4893
0.193548387096774
0.8833
0.8761
0.8445
0.7915
0.7405
0.4186
0.225806451612903
0.8766
0.8697
0.8443
0.7743
0.7313
0.4112
0.258064516129032
0.8583
0.8505
0.8206
0.7491
0.6953
0.411
0.290322580645161
0.8215
0.8148
0.7862
0.7263
0.6817
0.4028
0.32258064516129
0.7691
0.7629
0.7384
0.6825
0.6411
0.3866
0.354838709677419
0.7561
0.7498
0.7327
0.6806
0.6387
0.3778
11
0.387096774193548
0.7302
0.7241
0.7027
0.6494
0.6121
0.3582
0.419354838709677
0.7075
0.7018
0.6772
0.6266
0.5869
0.3532
0.451612903225806
0.6919
0.6861
0.6621
0.6096
0.5696
0.3414
0.483870967741936
0.6485
0.6428
0.6192
0.5792
0.5482
0.3171
0.516129032258065
0.6342
0.6289
0.6064
0.557
0.521
0.3135
0.548387096774194
0.6214
0.6159
0.5935
0.5454
0.5111
0.3042
0.580645161290323
0.6175
0.6124
0.5901
0.5449
0.5098
0.3031
0.612903225806452
0.6148
0.6097
0.5887
0.5405
0.5049
0.3028
0.645161290322581
0.6113
0.6064
0.5848
0.5387
0.5047
0.2912
0.67741935483871
0.5934
0.5884
0.5669
0.5366
0.5039
0.2867
0.709677419354839
0.587
0.5819
0.5609
0.5239
0.4911
0.286
0.741935483870968
0.5813
0.5766
0.5601
0.5183
0.4875
0.2858
0.774193548387097
0.5778
0.5731
0.5561
0.5154
0.4829
0.285
0.806451612903226
0.5769
0.5719
0.5527
0.5094
0.4746
0.284
0.838709677419355
0.5752
0.5701
0.5519
0.5068
0.4736
0.2732
0.870967741935484
0.5725
0.568
0.549
0.5068
0.4722
0.2722
0.903225806451613
0.5696
0.5648
0.5455
0.5024
0.4707
0.2696
0.935483870967742
0.5462
0.5418
0.5225
0.4794
0.4486
0.2691
0.967741935483871
0.4578
0.4529
0.436
0.4001
0.3741
0.189
0.1
1.2774
1.2674
1.2246
1.1289
1.05906
0.74906
Average
of
yearly
averages:
0.417833333333333
Inputs
generated
by
pe4.
pl
­
8­
August­
2003
Data
used
for
this
run:
Output
File:
CAcornF
Metfile:
w23232.
dvf
PRZM
scenario:
CAcornC.
txt
EXAMS
environment
file:
ir298.
exv
Chemical
Name:
Flumetsulam
Description
Variable
Name
Value
Units
Comments
Molecular
weight
mwt
325.3
g/
mol
Henry's
Law
Const.
henry
atm­
m^
3/
mol
Vapor
Pressure
vapr
0.8e­
15
torr
Solubility
sol
5650
mg/
L
Kd
Kd
mg/
L
Koc
Koc
27.23
mg/
L
Photolysis
half­
life
kdp
0
days
Half­
life
Aerobic
Aquatic
Metabolism
kbacw
197.6
days
Halfife
Anaerobic
Aquatic
Metabolism
kbacs
183
days
Halfife
Aerobic
Soil
Metabolism
asm
98.8
days
Halfife
Hydrolysis:
pH
7
0
days
Half­
life
Method:
CAM
1
integer
See
PRZM
manual
Incorporation
Depth:
DEPI
4
cm
12
Application
Rate:
TAPP
0.0784
kg/
ha
Application
Efficiency:
APPEFF
0.95
fraction
Spray
Drift
DRFT
0.16
fraction
of
application
rate
applied
to
pond
Application
Date
Date
24­
03
dd/
mm
or
dd/
mmm
or
dd­
mm
or
dd­
mmm
Record
17:
FILTRA
IPSCND
1
UPTKF
Record
18:
PLVKRT
PLDKRT
FEXTRC
0.5
Flag
for
Index
Res.
Run
IR
IR
Flag
for
runoff
calc.
RUNOFF
total
none,
monthly
or
total(
average
of
entire
run)
13
stored
as
MSsoyF.
out
Chemical:
Flumetsulam
PRZM
environment:
MSsoybeanC.
txt
modified
Satday,
12
October
2002
at
17:
07:
44
EXAMS
environment:
ir298.
exv
modified
Thuday,
29
August
2002
at
15:
34:
12
Metfile:
w13893.
dvf
modified
Wedday,
3
July
2002
at
09:
06:
20
Water
segment
concentrations
(
ppb)

Year
Peak
96
hr
21
Day
60
Day
90
Day
Yearly
1961
1.089
1.063
0.9887
0.8333
0.7276
0.2594
1962
0.5705
0.557
0.5045
0.442
0.3824
0.1414
1963
1.457
1.421
1.288
1.047
0.8902
0.3179
1964
2.261
2.206
2.009
1.616
1.372
0.484
1965
1.09
1.063
0.9574
0.7615
0.6498
0.2381
1966
0.5794
0.5708
0.5226
0.4535
0.4064
0.1536
1967
0.5148
0.5021
0.4819
0.4278
0.3735
0.1377
1968
1.067
1.041
0.9441
0.7619
0.6515
0.2291
1969
2.535
2.474
2.269
1.868
1.591
0.5585
1970
2.065
2.014
1.85
1.544
1.32
0.4744
1971
0.6698
0.6538
0.5909
0.5523
0.4848
0.1844
1972
1.476
1.44
1.3
1.072
0.9166
0.3262
1973
0.4791
0.4678
0.4501
0.3827
0.3283
0.1225
1974
0.6927
0.676
0.6186
0.5142
0.4488
0.1626
1975
0.8822
0.8609
0.7795
0.625
0.5442
0.1969
1976
0.4762
0.4646
0.4259
0.4034
0.356
0.1326
1977
1.967
1.918
1.73
1.381
1.169
0.4044
1978
0.6334
0.6177
0.5692
0.4926
0.4304
0.1616
1979
7.226
7.08
6.432
5.161
4.385
1.514
1980
2.089
2.051
1.902
1.534
1.302
0.4864
1981
0.8617
0.8397
0.7673
0.6253
0.5455
0.2028
1982
1.733
1.693
1.569
1.27
1.078
0.3768
1983
1.407
1.375
1.258
1.02
0.875
0.3131
1984
2.594
2.532
2.297
1.853
1.575
0.5509
1985
1.507
1.47
1.326
1.051
0.8864
0.3416
1986
2.208
2.154
1.945
1.552
1.313
0.4627
1987
1.615
1.576
1.424
1.127
0.9502
0.35
1988
1.354
1.322
1.209
0.9781
0.8307
0.2935
1989
0.866
0.8451
0.7638
0.6138
0.5257
0.1901
1990
0.8727
0.8518
0.8058
0.6703
0.5799
0.2077
Sorted
results
Prob.
Peak
96
hr
21
Day
60
Day
90
Day
Yearly
0.032258064516129
7.226
7.08
6.432
5.161
4.385
1.514
0.0645161290322581
2.594
2.532
2.297
1.868
1.591
0.5585
0.0967741935483871
2.535
2.474
2.269
1.853
1.575
0.5509
0.129032258064516
2.261
2.206
2.009
1.616
1.372
0.4864
0.161290322580645
2.208
2.154
1.945
1.552
1.32
0.484
0.193548387096774
2.089
2.051
1.902
1.544
1.313
0.4744
0.225806451612903
2.065
2.014
1.85
1.534
1.302
0.4627
0.258064516129032
1.967
1.918
1.73
1.381
1.169
0.4044
0.290322580645161
1.733
1.693
1.569
1.27
1.078
0.3768
0.32258064516129
1.615
1.576
1.424
1.127
0.9502
0.35
0.354838709677419
1.507
1.47
1.326
1.072
0.9166
0.3416
0.387096774193548
1.476
1.44
1.3
1.051
0.8902
0.3262
0.419354838709677
1.457
1.421
1.288
1.047
0.8864
0.3179
0.451612903225806
1.407
1.375
1.258
1.02
0.875
0.3131
0.483870967741936
1.354
1.322
1.209
0.9781
0.8307
0.2935
0.516129032258065
1.09
1.063
0.9887
0.8333
0.7276
0.2594
0.548387096774194
1.089
1.063
0.9574
0.7619
0.6515
0.2381
0.580645161290323
1.067
1.041
0.9441
0.7615
0.6498
0.2291
0.612903225806452
0.8822
0.8609
0.8058
0.6703
0.5799
14
0.2077
0.645161290322581
0.8727
0.8518
0.7795
0.6253
0.5455
0.2028
0.67741935483871
0.866
0.8451
0.7673
0.625
0.5442
0.1969
0.709677419354839
0.8617
0.8397
0.7638
0.6138
0.5257
0.1901
0.741935483870968
0.6927
0.676
0.6186
0.5523
0.4848
0.1844
0.774193548387097
0.6698
0.6538
0.5909
0.5142
0.4488
0.1626
0.806451612903226
0.6334
0.6177
0.5692
0.4926
0.4304
0.1616
0.838709677419355
0.5794
0.5708
0.5226
0.4535
0.4064
0.1536
0.870967741935484
0.5705
0.557
0.5045
0.442
0.3824
0.1414
0.903225806451613
0.5148
0.5021
0.4819
0.4278
0.3735
0.1377
0.935483870967742
0.4791
0.4678
0.4501
0.4034
0.356
0.1326
0.967741935483871
0.4762
0.4646
0.4259
0.3827
0.3283
0.1225
0.1
2.5076
2.4472
2.243
1.8293
1.5547
0.54445
Average
of
yearly
averages:
0.332496666666667
Inputs
generated
by
pe4.
pl
­
8­
August­
2003
Data
used
for
this
run:
Output
File:
MSsoyF
Metfile:
w13893.
dvf
PRZM
scenario:
MSsoybeanC.
txt
EXAMS
environment
file:
ir298.
exv
Chemical
Name:
Flumetsulam
Description
Variable
Name
Value
Units
Comments
Molecular
weight
mwt
325.3
g/
mol
Henry's
Law
Const.
henry
atm­
m^
3/
mol
Vapor
Pressure
vapr
0.8e­
15
torr
Solubility
sol
5650
mg/
L
Kd
Kd
mg/
L
Koc
Koc
27.23
mg/
L
Photolysis
half­
life
kdp
0
days
Half­
life
Aerobic
Aquatic
Metabolism
kbacw
197.6
days
Halfife
Anaerobic
Aquatic
Metabolism
kbacs
183
days
Halfife
Aerobic
Soil
Metabolism
asm
98.8
days
Halfife
Hydrolysis:
pH
7
0
days
Half­
life
Method:
CAM
1
integer
See
PRZM
manual
Incorporation
Depth:
DEPI
4
cm
Application
Rate:
TAPP
0.0784
kg/
ha
Application
Efficiency:
APPEFF
0.95
fraction
Spray
Drift
DRFT
0.16
fraction
of
application
rate
applied
to
pond
Application
Date
Date
31­
03
dd/
mm
or
dd/
mmm
or
dd­
mm
or
dd­
mmm
Record
17:
FILTRA
IPSCND
1
UPTKF
Record
18:
PLVKRT
PLDKRT
FEXTRC
0.5
Flag
for
Index
Res.
Run
IR
IR
Flag
for
runoff
calc.
RUNOFF
total
none,
monthly
or
total(
average
of
entire
run)
15
SCIGROW
input/
output
screen:
