Document ID: EPA-HQ-OPP-2002-0079-0009
Agency: epa
Document Type: Supporting & Related Material
Title: 
Posted Date: 2002-06-19T04:00Z

UNITED
STATES
ENVIRONMENTAL
PROTECTION
AGENCY
WASHINGTON,
D.
C.
20460
OFFICE
OF
PREVENTION,
PESTICIDES
AND
TOXIC
SUBSTANCES
Date:
1/
14/
02
MEMORANDUM:
Drinking
Water
Assessment
for
Linuron
metabolites
on
Carrots
in
California.

TO:
Carol
Christensen
Reregistration
actions
Branch
II
Health
Effects
Division
(7509C)

FROM:
Ibrahim
Abdel­
Saheb/
Agronomist
Environmental
Risk
Branch
II
Environmental
Fate
and
Effects
Division
(7507C)

PEER
REVIEW:
Ian
Kennedy/
Hydrologist
Environmental
Risk
Branch
II
Environmental
Fate
and
Effects
Division
(7507C)

THRU:
Tom
Bailey,
Branch
Chief
Environmental
Risk
Branch
II
Environmental
Fate
and
Effects
Division
(7507C)

Conclusions:

In
response
to
HED
request
(Carol
Christensen
on
12/
21/
01),
the
three
major
linuron
metabolites
*
formed
under
aerobic
soil
conditions
use
on
carrots
in
(EPA
Reg.
No.
1812­
320)
are
represented
by
this
memorandum.
The
degradate
3,4­
dichloroaniline
(3,4­
DCA)
was
not
included
in
this
assessment.
Based
on
the
results
from
the
aerobic
soil
metabolism
study
(MRID#
41625401),
the
degradate
3,4­
DCA
was
not
detected
(0.01
ppm
detection
limit).
According
to
acceptable
fate
studies,
3,4­
DCA
is
formed
under
anaerobic
aquatic
conditions
(conditions
rarely
found
in
the
environment
and/
or
relevant
to
drinking
water
assessment)
consisted
of
1.5%
of
the
applied
linuron.

*:(
3­(
3­,
4­
dichlorophenyl)­
1­
methoxyurea)
(desmethoxy
linuron),
(3­(
3­,
4­
dichlorophenyl)­
1­
methoxy­
1­
methylurea)
(desmethoxy
linuron),
and
1­(
3­,
4­
dichlorophenyl)
urea)
(norlinuron)
2
EFED
currently
has
no
monitoring
data
for
these
degradates
in
surface
or
groundwater.

The
Tier
II
screening
models
PRZM
1
and
EXAMS
2
with
the
Index
Reservoir
and
Percent
Crop
Area
adjustment
(IR­
PCA
PRZM/
EXAMS)
were
used
to
determine
estimated
surface
water
concentrations
of
the
linuron
metabolites
listed
above.
The
Screening
Concentration
in
Groundwater
(SCI­
GROW
3
)
model
was
used
to
estimate
groundwater
concentrations
for
linuron.
Modeling
results
are
shown
in
Table
1.

Table
1.
Estimated
environmental
concentrations
in
surface
and
groundwater
for
desmethyl
linuron,
demthoxy
linuron,
and
nor
linuron
use
on
carrots.

model
EECs
(µg/
L)

desmethyl
linuron
demthoxy
linuron
norlinuron
Surface
water/
peak
(90
th
percentile
annual
daily
max.)
1.69
3.26
1.26
Surface
water/
90
th
percentile
annual
mean)
1.60
3.10
1.20
Surface
water/
36­
year
overall
mean
1.17
2.28
0.88
Groundwater/
peak
and
long
term
average
0.047
0.094
0.035
use(
s)
modeled
two
applications
on
carrots
@
0.04
lb
ai/
acre,
ground
application
two
applications
on
carrots
@
0.08
lb
ai/
acre,
ground
application
two
applications
on
carrots
@
0.03
lb
ai/
acre,
ground
application
PCA
Default
PCA
(0.87)

The
IR­
PCA
PRZM/
EXAMS
modeling
results
indicate
that
desmethyl
linuron,
desmethoxy
linuron
and
norlinuron
have
the
potential
to
contaminate
surface
waters
by
spray
drift,
and
runoff
in
areas
with
large
amounts
of
annual
rainfall.
3
Environmental
Fate
and
Transport
Assessment
Although
the
environmental
fate
data
base
for
parent
linuron
is
essentially
complete,
two
environmental
fate
data
requirements
(leaching/
adsorption/
desorption
and
terrestrial
field
dissipation
studies)
are
not
fulfilled.
The
environmental
fate
assessment
for
linuron
is
incomplete
and
tentative
because
information
on
the
persistence,
mobility
and
dissipation
pathways
of
several
degradates
of
linuron
is
not
available.

Parent
linuron
appears
to
be
moderately
persistent
and
relatively
immobile.
Increased
mobility
may
occur
under
specific
environmental
conditions
such
as
in
coarse
textured
soils
and
soils
with
low
levels
of
organic
matter.
Linuron
dissipates
principally
by
biotic
processes
such
as
microbial
degradation.
In
surface
soils
with
adequate
organic
matter,
the
combined
processes
of
adsorption
and
microbial
degradation
would
limit
linuron's
potential
to
migrate
to
ground
water.
Linuron
could
runoff
to
surface
water
bodies.
In
that
case,
it
would
degrade
fairly
rapidly
to
three
primary
metabolites
(desmethoxy
linuron,
desmethyl
linuron,
norlinuron,
and
3,4­
DCA,
none
of
each
is
>10%
of
the
applied
linuron
in
the
aerobic
soil
metabolism
study).
However,
information
on
the
persistence
and
mobility
of
these
degradates
is
not
currently
available.

Linuron
exhibits
some
of
the
properties
and
characteristics
of
chemicals
that
have
been
detected
in
ground
water,
and
linuron
itself
has
been
detected
in
ground
water
in
four
states
(Georgia,
Missouri,
Virginia
and
Wisconsin).
Linuron
is
moderately
persistent
with
an
aerobic
soil
metabolism
half­
life
ranging
from
57
to
100
days.
Because
linuron
is
sufficiently
persistent
and
may
be
mobile
under
certain
environmental
conditions,
it
has
the
potential
to
impact
ground
water
quality.

Linuron
can
be
applied
aerially
or
by
ground
spray
and
therefore
could
contaminate
surface
waters
through
spray
drift.
It
has
the
potential
to
be
somewhat
persistent
in
surface
waters,
particularly
those
with
low
microbiological
activity
and
long
hydrological
residence
times.
In
a
lab
study,
linuron
degraded
with
a
half­
life
of
less
than
3
weeks
in
nonsterile
anaerobic
silt
loam
and
sand
soil:
water
(1:
1)
systems.
It
may
be
less
persistent
in
water
and
sediment
under
anaerobic
conditions
than
under
aerobic
conditions.
Its
bioconcentration
potential
is
relatively
low.

Linuron
is
not
currently
regulated
under
the
Safe
Drinking
Water
Act,
and
water
supply
systems
are
not
required
to
sample
4
and
analyze
for
it.
The
primary
treatment
processes
employed
by
most
water
systems
may
not
always
be
completely
effective
in
removing
linuron's
degradates.
As
a
result,
the
Agency
does
have
some
moderate
concerns
regarding
potential
risks
of
these
degradates
to
surface
water
source
supply
systems.

Surface
Water
Monitoring
The
EFED
currently
has
no
monitoring
data
on
the
concentrations
of
desmethyl
linuron,
desmethoxy
linuron
or
nor
linuron
in
surface
water.

Modeling
Tier
II
surface
water
modeling
was
done
using
the
Index
Reservoir
(IR)
scenario
and
Percent
Crop
Area
(PCA)
factor
applied
after
modeling.

The
index
reservoir
represents
a
potentially
vulnerable
drinking
water
source
based
on
the
geometry
of
an
actual
reservoir
and
its
watershed
in
a
specific
area
(Illinois),
using
regional
screening
specific
cropping
patterns,
weather,
soils,
and
other
factors.

The
PCA
is
a
generic
watershed­
based
adjustment
factor
which
represents
the
portion
of
a
watershed
planted
to
a
crop
or
crops
and
will
be
applied
to
pesticide
concentrations
estimated
for
the
surface
water
component
of
the
drinking
water
exposure
assessment
using
PRZM/
EXAMS
with
the
index
reservoir
scenario.

EFED
has
limited
fate
and
mobility
data
on
these
metabolites;
thus,
a
combined
residue
approach
was
used
to
calculate
their
aerobic
soil
metabolism
half­
lives
(assuming
equal
toxicity)
by
the
summation
of
the
concentrations
of
the
parent
and
its
metabolites.
The
IR­
PCA
PRZM/
EXAMS
model
use
and
fate
input
parameters
for
linuron
in
surface
water
are
shown
in
Table
2.
The
IR­
PCA
PRZM/
EXAMS
model
input
and
output
files
for
linuron
are
shown
in
Appendix
I.

Table
2:
IR­
PC
PRZM/
EXAMS
input
parameters
for
desmethyl
linuron,
desmethoxy
linuron,
and
nor
linuron
use
on
carrots
in
California.

Input
variable
Input
value
&
calculations
Source/
Quality
of
data
Crop
name
carrots
carrots
carrots
label
EPA
Reg.
No.
1812­
320).
5
application
rate
(lb
ai/
acre)
0.04
0.08
0.03
label
EPA
Reg.
No.
1812­
320).
Linuron
application
rate
X
[the
maximum
conversion
rate
from
the
degradation
of
Linuron
to
degradate
in
aerobic
soil
metabolism
studies)
x(
the
molecular
weight
ratio
of
degradate
to
parent)].

Interval
between
appl.
(d)
14
14
14
label
EPA
Reg.
No.
1812­
320).

A
p
p
l
i
c
a
t
i
o
n
efficiency
0.99
0.99
0.99
IR­
PCA
Guidance
8
S
p
r
a
y
d
r
i
f
t
fraction
0.064
0.064
0.064
IR­
PCA
Guidance
Application
method
ground
ground
ground
label
(EPA
Reg.
No.
1812­
362).

DWRATE
(day
­1
)
0.002
0.002
0.002
MRID#
41625401;
combined
residue
calculation,
Input
parameters
guidance
9
;
single
value
X
3.

DSRATE
(day
­1
)
0.002
0.002
0.002
MRID#
41625401;
combined
residue
calculation
Input
parameters
guidance;
single
value
X
3
Kd
(mL/
g)
0
*
0
0
No
data
available
Henry
(atm.
m
3
/mole)
6.07X10
­8
(calculate
d)
6.07X10
­8
(calcula
ted)
6.07X10
8
(calcul
ated)
RED,
1994.
Value
for
the
parent
(linuron)
was
used.

KBACW
(h
­1
)
0.001
0.001
0.001
No
aerobic
aquatic
data
is
available,
the
aerobic
soil
met.

degradation
rate
was
multiplied
by
0.5.
MRID#
41625401.
Input
parameters
guidance.

KBACS
(h
­1
)
0.0004
0.0004
0.0004
Anaerobic
aquatic
half­
life
(21
days)
was
multiplied
by
3.
MRID#
40142501.
Input
parameters
guidance
.

KDP
(h
­1
)
0.0006
0.0006
0.0006
MRID#
40103601;
Input
parameters
guidance.

KBH,
KNH,
KAH
(h
­1
)
(stable)
(stable)
(stable
)
MRID#
40916201;
Input
parameters
guidance.
Value
for
parent
used.

KPS
(mL/
g)
0
0
0
MRID#
00148443;
Input
parameters
guidance.

MWT
(g/
mole)
235.1
219.1
205.1
RED,
1994.

Solubility
@
25
0
C
(ppm)
81
81
81
RED,
1994.
Value
for
parent
used.

Vapor
pressure
(torr)
1.5X10
­5
1.5X10
­5
1.5X10
­5
The
MERCK
Index
10
.
Value
for
parent
used.

*:
Preliminary
modeling
using
Kd
of
0
and
2.7
resulted
in
little
difference
in
EEC's.
A
Kd
of
0
was
used
in
this
assessment
as
a
worse
scenario
condition.
6
Assumptions
and
Uncertainties
11,12
In
general,
the
use
of
input
parameter
values
for
the
parent
may
increase
the
uncertainties
in
this
assessment.

Index
Reservoir
The
Index
reservoir
represent
potential
drinking
water
exposure
from
a
specific
area
(Illinois)
with
specific
cropping
patterns,
weather,
soils,
and
other
factors.
Use
of
the
index
reservoir
for
areas
with
different
climates,
crops,
pesticides
used,
sources
of
water
(e.
g.
rivers
instead
of
reservoirs,
etc),
and
hydrogeology
creates
uncertainties.
In
general,
because
the
index
reservoir
represents
a
fairly
vulnerable
watershed,
the
exposure
estimated
with
the
index
reservoir
will
likely
be
higher
than
the
actual
exposure
for
most
drinking
water
sources.
However,
the
index
reservoir
is
not
a
worst
case
scenario,
communities
that
derive
their
drinking
water
from
smaller
bodies
of
water
with
minimal
outflow,
or
with
more
runoff
prone
soils
would
likely
get
higher
drinking
water
exposure
than
estimated
using
the
index
reservoir.
Areas
with
a
more
humid
climate
that
use
a
similar
reservoir
and
cropping
patterns
may
also
get
more
pesticides
in
their
drinking
water
than
predicted
using
this
scenario.

PRZM/
EXAMS
uses
the
characteristics
of
a
single
soil
to
represent
the
soil
in
the
basin.
In
fact,
soils
can
vary
substantially
across
even
small
areas,
and
this
variation
is
not
reflected
in
these
simulations.

PRZM/
EXAMS
does
not
consider
tile
drainage.
Areas
that
are
prone
to
substantial
runoff
are
often
tile
drained.
Tile
drainage
contributes
additional
water
and
in
some
cases,
additional
pesticide
loading
to
the
reservoir.
This
may
cause
either
an
increase
or
decrease
in
the
pesticide
concentration
in
the
reservoir.
Tile
drainage
also
causes
the
surface
soil
to
dry
out
faster.
This
will
reduce
runoff
of
the
pesticide
into
the
reservoir.
The
watershed
used
as
the
model
for
the
index
reservoir
(Shipman
City
Lake)
does
not
have
tile
drainage
in
the
cropped
areas.

EXAMS
is
unable
to
easily
model
spring
and
fall
turnover.
Turnover
occurs
when
the
temperature
drops
in
the
fall
and
the
thermal
stratification
of
the
reservoir
is
removed.
Turnover
occurs
again
in
the
spring
when
the
reservoir
warms
up.
This
results
in
complete
mixing
of
the
chemical
through
the
water
column
at
these
times.
Because
of
this
inability,
the
Index
Reservoir
has
been
simulated
without
stratification.
There
is
7
data
to
suggest
that
Shipman
City
Lake,
upon
which
the
Index
Reservoir
is
based,
does
indeed
stratify
in
the
deepest
parts
of
the
lake
at
least
in
some
years.
This
may
result
in
over
or
underestimation
of
the
concentration
in
drinking
water
depending
upon
the
time
of
the
year
and
the
depth
the
drinking
water
intake
is
drawing
from.

Percent
Crop
Area
Correction
Factor
The
PCA
is
a
watershed­
based
modification.
Implicit
in
its
application
is
the
assumption
that
currently­
used
field­
scale
models
reflect
basin­
scale
processes
consistently
for
all
pesticides
and
uses.
In
other
words,
we
assume
the
field
scale
processes
simulated
by
the
coupled
PRZM
and
EXAMS
models
are
a
reasonable
approximation
of
pesticide
fate
and
transport
within
a
watershed
that
contains
a
drinking
water
reservoir.
If
the
models
fail
to
capture
pertinent
basin­
scale
fate
and
transport
processes
consistently
for
all
pesticides
and
all
uses,
the
application
of
a
factor
that
reduces
the
estimated
concentrations
predicted
by
modeling
could,
in
some
instances,
result
in
inadvertently
passing
a
chemical
through
the
screen
that
may
actually
pose
a
risk.
Some
preliminary
assessments
made
in
the
development
of
the
PCA
suggest
that
PRZM/
EXAMS
may
not
be
realistically
capturing
basin­
scale
processes
for
all
pesticides
or
for
all
uses.
A
preliminary
survey
of
water
assessments
which
compared
screening
model
estimates
to
readily
available
monitoring
data
suggest
uneven
model
results.
In
some
instances,
the
screening
model
estimates
are
more
than
an
order
of
magnitude
greater
than
the
highest
concentrations
reported
in
available
monitoring
data;
in
other
instances,
the
model
estimates
are
less
than
monitoring
concentrations.
Because
of
these
concerns,
the
Science
Advisory
Panel
(SAP)
recommended
using
the
PCA
only
for
"major"
crops
in
the
Midwest.
For
other
crops,
development
of
PCA's
will
depend
on
the
availability
of
relevant
monitoring
data
that
could
be
used
to
evaluate
the
result
of
the
PCA
adjustment.

The
spatial
data
used
for
the
PCA
came
from
readily­
available
sources
and
have
a
number
of
inherent
limitations:

°
The
size
of
the
8­
digit
HUC
[mean
=
366,989
ha;
range
=
6.7­
2,282,081
ha;
n
=
2,111]
may
not
provide
reasonable
estimates
of
actual
PCA's
for
smaller
watersheds.
The
watersheds
that
drain
into
drinking
water
reservoirs
are
generally
smaller
than
the
8­
digit
HUC
and
may
be
better
represented
by
watersheds
defined
for
drinking
water
intakes.
8
°
The
conversion
of
the
county
level
data
to
watershed­
based
percent
crop
areas
assumes
the
distribution
of
the
crops
within
a
county
is
uniform
and
homogeneous
throughout
the
county
area.
Distance
between
the
treated
fields
and
the
water
body
is
not
addressed.
°
The
PCA's
were
generated
using
data
from
the
1992
Census
of
Agriculture.
However,
recent
changes
in
the
agriculture
sector
from
farm
bill
legislation
may
significantly
impact
the
distribution
of
crops
throughout
the
country.
The
methods
described
in
this
report
can
rapidly
be
updated
as
more
current
agricultural
crops
data
are
obtained.
The
assumption
that
yearly
changes
in
cropping
patterns
will
cause
minimal
impact
needs
to
be
evaluated.

The
PCA
adjustment
is
only
applicable
to
pesticides
applied
to
agricultural
crops.
Contributions
to
surface
waters
from
nonagricultural
uses
such
as
urban
environments
are
not
wellmodeled
Currently,
non­
agricultural
uses
are
not
included
in
the
screening
model
assessments
for
drinking
water.

The
PCA
does
not
consider
percent
crop
treated
because
detailed
pesticide
usage
data
are
extremely
limited
at
this
time.
Detailed
pesticide
usage
data
are
currently
available
for
only
a
few
states.

Groundwater
Monitoring
The
EFED
has
no
monitoring
data
on
the
concentrations
of
desmethyl
linuron,
desmethoxy
linuron
or
nor
linuron
in
groundwater
at
the
present
time.

There
is
a
possibility
that
those
metabolites
were
not
intended
to
look
for,
or
they
might
have
been
present
at
concentrations
lower
than
that
of
the
instruments
used
for
the
water
samples
collected
The
SCI­
GROW
model
was
used
to
estimate
potential
groundwater
concentrations
of
linuron.

Table
3
shows
the
input
parameter
values
used
in
SCI­
GROW
modeling.

Table
3.
Input
parameters
for
desmethyl
linuron,
desmethoxy
linuron,
and
nor
linuron
used
in
the
SCI­
GROW
model.
9
Input
variable
Input
value
&
calculations
Source/
Quality
of
data
1
Application
rate
(lb
ai/
acre)
0.0
4
0.0
8
0.0
3
(EPA
Reg.
No.
1812­
320).

Maximum
No.
of
Applications
2
2
2
(EPA
Reg.
No.
1812­
320).

Koc
(mL/
g)
208
208
208
MRID#
46007015
(median
value
for
parent);
Input
parameters
guidance.

Aerobic
Soil
metabolism
t1/
2.

(day)
99
99
99
MRID#
41625401;
combined
residue
calculations,
Input
parameters
guidance.

Groundwater
EECs
predicted
using
the
SCI­
GROW
screening
model
are
substantially
less
than
those
estimated
for
surface
water
using
PRZM
and
EXAMS.
However,
persistence
in
groundwater
should
be
longer.

REFERENCES
1.
Carsel,
R.
F.,
J.
C.
Imhoff,
P.
R.
Hummel,
J.
M.
Cheplick
and
J.
S.
Donigian,
Jr.
1997.
PRZM­
3,
A
Model
for
Predicting
Pesticide
and
Nitrogen
Fate
in
Crop
Root
and
Unsaturated
Soil
Zones:
Users
Manual
for
Release
3.0;
Environmental
Research
Laboratory,
Office
of
Research
and
Development,
U.
S.
Environmental
Protection
Agency,
Athens,
GA.

2.
Burns,
L.
A.
March
1997.
Exposure
Analysis
Modeling
System
(EXAMSII)
Users
Guide
for
Version
2.97.5,
Environmental
Research
Laboratory,
Office
of
Research
and
Development,
U.
S.
Environmental
Protection
Agency,
Athens,
GA.

3.
Barrett,
M.,
1997,
Proposal
For
a
Method
to
Determine
Screening
Concentration
Estimates
for
Drinking
Water
Derived
from
Groundwater
Studies,
EFED/
OPP.

4.
U.
S
GS.
1992.
National
Water
Quality
Assessment
(NWQA),
Pesticides
National
Synthesis
Project,
Annual
Use:
Linuron.

5.
U.
S
GS.
1993.
National
Water
Quality
Assessment
Program
San
Joaquin
­
Tulare
Basins
Study
Unit,
[Online].
Available
at
http://
ca.
water.
usgs.
gov/
sanj_
nawqa/
data_
sw/
ifs.
1993.
herb2.

6.
The
United
State
Department
of
Agriculture,
Office
of
Pesticide
Management
Policy
&
Pesticide
Impact
Assessment
Program.
Crop
Profile
for
Carrots
in
California,
[Online].
A
v
a
i
l
a
b
l
e
a
t
http://
pestdata.
ncsu.
edu/
cropprofiles/
Detail.
CFM?
FactShee
10
ts_
RecordID=
285.

7.
USGS.
1998.
Pesticides
in
Surface
and
Ground
Water
of
the
United
States:
Summary
of
Results
of
the
National
Water
Quality
Assessment
Program,
[Online].
Available
at
http://(
NAWQA)=
http://
ca.
water.
usgs.
gov/
pnsp/
allsum/#
t1.

8.
Effland,
W.,
N.
Thurman,
I.
Kennedy,
R.
D.
Jones,
J.
Breithaupt,
J.
Lin,
J.
Carleton,
L.
Libel.
R.
Parker,
and
R.
Matzner.
2000.
"
Guidance
for
use
of
the
index
Reservoir
and
Percent
Crop
Area
Factor
in
drinking
water
exposure
assessment
s.
Office
of
Pesticide
Programs.

9.
Guidance
for
Chemistry
and
Management
Practice
Input
Parameters
For
Use
in
Modeling
the
Environmental
Fate
and
Transport
of
Pesticides.
Version
2.
November
7,
2000.
U.
S.
EPA
Office
of
Pesticide
Programs,
Environmental
Fate
and
Effects
Division.

10.
The
Merck
Index.
1989.
An
encyclopedia
of
chemicals,
drugs,
and
biologicals.
11
th
ed.
Rahway,
N.
J.
p.
533.

11.
Carsel,
R.
F.,
J.
C.
Imhoff,
P.
R.
Hummel,
J.
M.
Cheplick
and
J.
S.
Donigian,
Jr.
1997.
PRZM­
3,
A
Model
for
Predicting
Pesticide
and
Nitrogen
Fate
in
Crop
Root
and
Unsaturated
Soil
Zones:
Users
Manual
for
Release
3.0;
Environmental
Research
Laboratory,
Office
of
Research
and
Development,
U.
S.
Environmental
Protection
Agency,
Athens,
GA.

12.
U.
S.
Environmental
Protection
Agency.
1984.
Chemical
Information
Fact
Sheet
Number
28:
Linuron.
Office
of
Pesticides
and
Toxic
Substances,
Washington,
DC,
9­
13.

13.
U.
S.
EPA.
1992.
Pesticides
in
Ground
Water
Database­
A
compilation
of
Monitoring
Studies:
1971
­
1991.
Office
of
Prevention,
Pesticides,
and
Toxic
Substances,
EPA
734­
12­
92­
001.

14.
U.
S
GS.
1998.
National
Water
Quality
Assessment
(NWQA),
Pesticides
National
Synthesis
Project
[Online]
at
http://
ca.
water.
usgs.
gov/
pnsp/
allsum/#
over.

APPENDIX
I
IR­
PCA
PRZM/
EXAMS
INPUT
FILE
FOR
THE
USE
OF
DESMETHYL
LINURON
ON
CARROTS
IN
CALIFORNIA
11
WTR
WTR
***********************************
WTR
*
PESTICIDE
ROOT
ZONE
MODEL
*
WTR
*
RELEASE
3.12
Beta
*
WTR
*
February
1998
*
WTR
***********************************
WTR
WTR
***********************************
WTR
WTR
DEVELOPED
FOR:
WTR
U.
S.
ENVIRONMENTAL
PROTECTION
AGENCY
WTR
OFFICE
OF
RESEARCH
AND
DEVELOPMENT
WTR
NATIONAL
EXPOSURE
RESEARCH
LABORATORY
WTR
ECOSYSTEMS
RESEARCH
DIVISION
WTR
ATHENS,
GEORGIA
30605­
2700
WTR
706/
355­
8328
WTR
Distributed
by:
Des
Center
for
Exposure
Assessment
Modeling
WTR
http://
www.
epa.
gov/
CEAM
WTR
ceam@
epamail.
epa.
gov
WTR
WTR
WTR
WTR
SIMULATION
START
DATE
(DAY­
MONTH­
YEAR)
1
JAN.,
48
WTR
SIMULATION
END
DATE
(DAY­
MONTH­
YEAR)
31
DEC.,
83
WTR
WTR
WTR
"Lerdo
clay
loam,
MLRA
C­
17;
Central
Valley,
CA,
Carrots"

WTR
WTR
WTR
WTR
WTR
WTR
HYDROLOGY
AND
SEDIMENT
RELATED
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
PAN
COEFFICIENT
FOR
EVAPORATION
0.7000
WTR
FLAG
FOR
ET
SOURCE
(0=
EVAP,
1=
TEMP,
2=
EITHER)
0
WTR
DEPTH
TO
WHICH
ET
IS
COMPUTED
YEAR­
ROUND
(CM)
17.0000
WTR
SNOW
MELT
COEFFICIENT
(CM/
DEG­
C­
DAY)
0.5000
WTR
INITIAL
CROP
NUMBER
1
WTR
INITIAL
CROP
CONDITION
1
WTR
WTR
WTR
SOIL
EROSION
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
USLE
"K"
PARAMETER
0.2100
WTR
USLE
"LS"
PARAMETER
1.000
WTR
USLE
"P"
PARAMETER
1.000
12
WTR
FIELD
OR
PLOT
AREA
(HA)
172.0
WTR
STORM
TYPE
3
WTR
SLOPE
1.000
WTR
HYDRAULIC
LENGTH
(M)
600.0
WTR
WTR
WTR
CROPPING
EROSION
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
WTR
CROP
NUMBER
1
WTR
NUMBER
OF
USLEC
FACTORS
3
WTR
WTR
#
DAY
MONTH
USLEC
MANNINGS
N
WTR
WTR
1
1
1
0.100
0.020
WTR
2
21
9
0.100
0.000
WTR
3
22
9
0.100
*****
WTR
WTR
WTR
CROP
INFORMATION
WTR
­­­­­­­­­­­­­­­

WTR
WTR
MAXIMUM
SURFACE
WTR
INTERCEPT.
MAXIMUM
MAXIMUM
MAXIMUM
CONDITION
MAXIMUM
WTR
CROP
POTENTIAL
ROOT
DEPTH
COVER
WEIGHT
AFTER
HEIGHT
AMC
RUNOFF
CURVE
NUMBERS
WTR
NUMBER
(CM)
(CM)
(%)
(KG/
M**
2)
HARVEST
(CM)
FALLOW
CROP
RESIDUE
WTR
WTR
I
80
70
75
WTR
1
0.2000
60.00
80.00
0.0000
3
100.000
II
91
85
88
WTR
III
96
93
95
WTR
WTR
WTR
CROP
ROTATION
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
CROP
EMERGENCE
MATURATION
HARVEST
WTR
NUMBER
DATE
DATE
DATE
WTR
WTR
1
10
SEP.,
49
23
DEC.,
49
31
DEC.,
48
WTR
1
10
SEP.,
50
23
DEC.,
50
31
DEC.,
49
WTR
1
10
SEP.,
51
23
DEC.,
51
31
DEC.,
50
WTR
1
10
SEP.,
52
23
DEC.,
52
31
DEC.,
51
WTR
1
10
SEP.,
53
23
DEC.,
53
31
DEC.,
52
WTR
1
10
SEP.,
54
23
DEC.,
54
31
DEC.,
53
WTR
1
10
SEP.,
55
23
DEC.,
55
31
DEC.,
54
WTR
1
10
SEP.,
56
23
DEC.,
56
31
DEC.,
55
WTR
1
10
SEP.,
57
23
DEC.,
57
31
DEC.,
56
WTR
1
10
SEP.,
58
23
DEC.,
58
31
DEC.,
57
WTR
1
10
SEP.,
59
23
DEC.,
59
31
DEC.,
58
13
WTR
1
10
SEP.,
60
23
DEC.,
60
31
DEC.,
59
WTR
1
10
SEP.,
61
23
DEC.,
61
31
DEC.,
60
WTR
1
10
SEP.,
62
23
DEC.,
62
31
DEC.,
61
WTR
1
10
SEP.,
63
23
DEC.,
63
31
DEC.,
62
WTR
1
10
SEP.,
64
23
DEC.,
64
31
DEC.,
63
WTR
1
10
SEP.,
65
23
DEC.,
65
31
DEC.,
64
WTR
1
10
SEP.,
66
23
DEC.,
66
31
DEC.,
65
WTR
1
10
SEP.,
67
23
DEC.,
67
31
DEC.,
66
WTR
1
10
SEP.,
68
23
DEC.,
68
31
DEC.,
67
WTR
1
10
SEP.,
69
23
DEC.,
69
31
DEC.,
68
WTR
1
10
SEP.,
70
23
DEC.,
70
31
DEC.,
69
WTR
1
10
SEP.,
71
23
DEC.,
71
31
DEC.,
70
WTR
1
10
SEP.,
72
23
DEC.,
72
31
DEC.,
71
WTR
1
10
SEP.,
73
23
DEC.,
73
31
DEC.,
72
WTR
1
10
SEP.,
74
23
DEC.,
74
31
DEC.,
73
WTR
1
10
SEP.,
75
23
DEC.,
75
31
DEC.,
74
WTR
1
10
SEP.,
76
23
DEC.,
76
31
DEC.,
75
WTR
1
10
SEP.,
77
23
DEC.,
77
31
DEC.,
76
WTR
1
10
SEP.,
78
23
DEC.,
78
31
DEC.,
77
WTR
1
10
SEP.,
79
23
DEC.,
79
31
DEC.,
78
WTR
1
10
SEP.,
80
23
DEC.,
80
31
DEC.,
79
WTR
1
10
SEP.,
81
23
DEC.,
81
31
DEC.,
80
WTR
1
10
SEP.,
82
23
DEC.,
82
31
DEC.,
81
WTR
1
10
SEP.,
83
23
DEC.,
83
31
DEC.,
82
WTR
1
10
SEP.,
84
23
DEC.,
84
31
DEC.,
83
WTR
WTR
WTR
desmethyl­
linuron
­
2
applications
@
.08
kg/
ha
WTR
WTR
WTR
WTR
WTR
WTR
PESTICIDE
APPLICATION
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
CHEMICAL
PESTICIDE
INCORPORATION
WTR
PESICIDE
APPLICATION
APPLICATION
APPLIED
DEPTH
WTR
NAME
DATE
MODEL
(KG/
HA)
(CM)
WTR
WTR
desmethyl­
linuron
10
DEC.,
48
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
48
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
49
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
49
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
50
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
50
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
51
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
51
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
52
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
52
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
53
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
53
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
54
2
0.8000E­
01
0.0000
14
WTR
desmethyl­
linuron
24
DEC.,
54
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
55
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
55
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
56
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
56
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
57
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
57
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
58
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
58
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
59
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
59
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
60
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
60
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
61
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
61
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
62
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
62
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
63
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
63
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
64
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
64
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
65
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
65
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
66
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
66
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
67
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
67
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
68
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
68
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
69
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
69
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
70
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
70
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
71
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
71
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
72
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
72
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
73
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
73
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
74
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
74
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
75
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
75
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
76
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
76
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
77
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
77
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
78
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
78
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
79
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
79
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
80
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
80
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
81
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
81
2
0.8000E­
01
0.0000
15
WTR
desmethyl­
linuron
10
DEC.,
82
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
82
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
83
2
0.8000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
83
2
0.8000E­
01
0.0000
WTR
WTR
WTR
WTR
PLANT
PESTICIDE
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
WTR
FOLIAR
PESTICIDE
DECAY
RATE
(/
DAY)
0.0000
WTR
EXTRACTION
COEFFICIENT
(/
CM)
0.0000
WTR
FOLIAR
PESTICIDE
VOLATILIZATION
RATE
(/
DAY)
0.0000
WTR
FILTRATION
PARAMETER
(M**
2/
MG)
0.0000
WTR
AFTER
HARVEST
DATE,
REMAINING
CHEMICAL
1
IN
CANOPY
IS
SURFACE
APPLIED
WTR
PLANT
UPTAKE
EFFICIENCY
FACTOR
0.0000
WTR
WTR
WTR
Linuron
WTR
WTR
WTR
WTR
WTR
WTR
GENERAL
SOIL
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
CORE
DEPTH
(CM)
100.0
WTR
TOTAL
HORIZONS
IN
CORE
2
WTR
THETA
FLAG
(0=
INPUT,
1=
CALCULATED)
0
WTR
PARTITION
COEFFICIENT
FLAG
(0=
INPUT,
1=
CALCULATED)
1
WTR
BULK
DENSITY
FLAG
(0=
INPUT,
1=
CALCULATED)
0
WTR
SOIL
HYDRAULICS
MODULE
(0=
HYDR1,1=
HYDR2)
0
WTR
TRANSPORT
SOLUTION
TECHNIQUE
(0=
BACKDIFF,
1=
MOC)
0
WTR
IRRIGATION
FLAG
(0=
OFF,
1=
ON)
0
WTR
TEMPERATURE
CORRECTION
(0=
OFF,
1=
ON)
0
WTR
THERMAL
CONDUCTIVITY
(0=
SUPPLIED,
1=
CALCULATED)
0
WTR
BIODEGRADATION
FLAG
(0=
OFF,
1=
ON)
0
WTR
WTR
PESTICIDE
PROPERTY
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
HENRY'S
LAW
CONSTANT
0.0000
WTR
DIFFUSION
COEFFICIENT
(CM**
2/
DAY)
0.0000
WTR
WTR
WTR
WTR
WTR
SOIL
HORIZON
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
INITIAL
FIELD
WILTING
WTR
SOIL
16
CAPACITY
POINT
WTR
BULK
WATER
DRAINAGE
LAT
DRAIN
WATER
WATORGANIC
WTR
HORI­
THICK
DENSITY
CONTENT
PARAMETER
PARAMETER
CONTENT
CONTENT
CARBON
WTR
ZON
(CM)
(G/
CM**
3)
(CM/
CM)
(/
DAY)
(/
DAY)
(CM/
CM)
(CM/
CM)
(%)
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
1
18.0
1.6000
0.325
0.00
0.00
.32500
0.175
0.017
WTR
2
82.0
1.5000
0.249
0.00
0.00
.24900
0.129
0.002
WTR
WTR
WTR
HORIZON
LAYER
DEPTH
(CM)
WTR
WTR
1
1.00
WTR
2
1.00
WTR
WTR
desmethyl­
linuron
WTR
WTR
HORIZON
1
WTR
­­­­­­

WTR
WTR
LIQUID
PHASE
DECAY
RATE
(/
DAY)
0.000
WTR
SOLID
PHASE
DECAY
RATE
(/
DAY)
0.000
WTR
GAS
PHASE
DECAY
RATE
(/
DAY)
0.000
WTR
DISPERSION
COEFFICIENTS
(CM**
2/
DAY)
0.000
WTR
WTR
HORIZON
2
WTR
­­­­­­

WTR
WTR
LIQUID
PHASE
DECAY
RATE
(/
DAY)
0.000
WTR
SOLID
PHASE
DECAY
RATE
(/
DAY)
0.000
WTR
GAS
PHASE
DECAY
RATE
(/
DAY)
0.000
WTR
DISPERSION
COEFFICIENTS
(CM**
2/
DAY)
0.000
WTR
WTR
WTR
WTR
PLOT
FILE
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­

WTR
WTR
NUMBER
OF
PLOTTING
VARIABLES
7
WTR
TIMSER
NAME
MODE
CMPT
BEG
CMPT
END
CONSTANT
TYPE
DSN
WTR
WTR
PRCP
TCUM
0
0
0.0000
P
WTR
RUNF
TCUM
0
0
0.0000
P
WTR
INFL
TCUM
1
1
0.0000
17
P
WTR
ESLS
TCUM
0
0
1000.
P
WTR
RFLX
TCUM
0
0
0.1000E+
06
P
WTR
EFLX
TCUM
0
0
0.1000E+
06
P
WTR
RZFX
TCUM
0
0
0.1000E+
06
P
OUT
1948
12
31
24
0
0.0000
0.0000
0.0000
0.0000
OUT
1949
12
31
24
0
0.7272E­
02
0.2764E­
05
0.1450E­
04
0.0000
OUT
1950
12
31
24
0
0.1715E­
04
0.7148E­
08
0.0000
0.0000
OUT
1951
12
31
24
0
0.2451E­
04
0.1065E­
07
0.3223E­
01
0.0000
OUT
1952
12
31
24
0
0.5911E­
03
0.5074E­
06
0.0000
0.0000
OUT
1953
12
31
24
0
0.2277E­
03
0.1693E­
06
0.0000
0.0000
OUT
1954
12
31
24
0
0.5584E­
03
0.4811E­
06
0.4856E­
02
0.0000
OUT
1955
12
31
24
0
0.4446E­
04
0.1990E­
07
0.0000
0.0000
OUT
1956
12
31
24
0
0.3226E­
05
0.1185E­
08
0.0000
0.0000
OUT
1957
12
31
24
0
0.1621E­
04
0.6704E­
08
0.1327
0.0000
OUT
1958
12
31
24
0
0.1110E­
04
0.4766E­
08
0.0000
0.0000
OUT
1959
12
31
24
0
0.1465E­
03
0.8693E­
07
0.7153E­
01
0.0000
OUT
1960
12
31
24
0
0.3714E­
05
0.1540E­
08
0.2880E­
01
0.0000
OUT
1961
12
31
24
0
0.9531E­
05
0.3627E­
08
0.9078E­
01
0.0000
OUT
1962
12
31
24
0
0.9341E­
04
0.5453E­
07
0.9446E­
01
0.0000
OUT
1963
12
31
24
0
0.1914E­
03
0.1262E­
06
0.2423E­
02
0.0000
OUT
1964
12
31
24
0
0.1466E­
03
0.1059E­
06
0.2264E­
01
0.0000
OUT
1965
12
31
24
0
0.1442E­
03
0.1015E­
06
0.2508
0.0000
OUT
1966
12
31
24
0
0.1344E­
04
0.7784E­
08
0.0000
0.0000
OUT
1967
12
31
24
0
0.2532E­
03
0.2033E­
06
0.4021E­
01
0.0000
OUT
1968
12
31
24
0
0.3737E­
03
0.3214E­
06
0.1983E­
01
0.0000
OUT
1969
12
31
24
0
0.1415E­
03
0.1011E­
06
0.3613E­
01
0.0000
OUT
1970
12
31
24
0
0.1417E­
03
0.9263E­
07
0.3688E­
01
0.0000
18
OUT
1971
12
31
24
0
0.3487E­
04
0.1695E­
07
0.3186E­
01
0.0000
OUT
1972
12
31
24
0
0.1316E­
03
0.8437E­
07
0.1019
0.0000
OUT
1973
12
31
24
0
0.2615E­
04
0.1424E­
07
0.5410E­
01
0.0000
OUT
1974
12
31
24
0
0.2504E­
03
0.1762E­
06
0.1996E­
02
0.0000
OUT
1975
12
31
24
0
0.3815E­
04
0.2029E­
07
0.2573E­
02
0.0000
OUT
1976
12
31
24
0
0.9317E­
05
0.4169E­
08
0.0000
0.0000
OUT
1977
12
31
24
0
0.5604E­
04
0.3121E­
07
0.4435E­
01
0.0000
OUT
1978
12
31
24
0
0.9286E­
04
0.5833E­
07
0.2292E­
01
0.0000
OUT
1979
12
31
24
0
0.8713E­
04
0.4885E­
07
0.3489E­
01
0.0000
OUT
1980
12
31
24
0
0.7427E­
05
0.2852E­
08
0.5095E­
01
0.0000
OUT
1981
12
31
24
0
0.1472E­
04
0.8863E­
08
0.0000
0.0000
OUT
1982
12
31
24
0
0.4429E­
04
0.2505E­
07
0.3448E­
01
0.0000
OUT
1983
12
31
24
0
0.3898E­
04
0.2235E­
07
0.3803E­
02
0.0000
IR­
PCA
PRZM/
EXAMS
OUTPUT
FILE
FOR
THE
USE
OF
DESMETHYL
LINURON
ON
CARROTS
IN
CALIFORNIA
Chemical:
desmethyl­
linuron
PRZM
environment:
dsmthl1.
txt
EXAMS
environment:
IRPRZM0.
EXV
Metfile:
met17.
met
Water
segment
concentrations
(ppb)

Year
Peak
96
hr
21
Day
60
Day
90
Day
Yearly
1948
0.1866
0.1865
0.1288
0.046620.03108
0.008098
1949
0.3617
0.3615
0.304
0.2228
0.2078
0.1896
1950
0.5276
0.5273
0.47
0.3897
0.3751
0.3602
1951
0.6856
0.6837
0.6263
0.5467
0.5327
0.5219
1952
0.8373
0.8327
0.7558
0.6753
0.6705
0.6532
1953
0.9711
0.9705
0.9139
0.8359
0.8324
0.8194
1954
1.236
1.235
1.179
1.111
1.108
1.085
1955
1.346
1.345
1.289
1.231
1.227
1.206
1956
1.363
1.362
1.342
1.34
1.337
1.294
1957
1.504
1.502
1.439
1.367
1.364
1.342
1958
1.496
1.496
1.495
1.493
1.482
1.356
1959
1.551
1.55
1.494
1.444
1.441
1.417
1960
1.584
1.582
1.577
1.567
1.562
1.508
19
1961
1.578
1.577
1.521
1.473
1.47
1.445
1962
1.574
1.574
1.574
1.517
1.459
1.355
1963
1.545
1.544
1.488
1.463
1.456
1.417
1964
1.64
1.639
1.584
1.539
1.536
1.509
1965
1.821
1.764
1.636
1.633
1.626
1.569
1966
1.81
1.808
1.801
1.781
1.765
1.715
1967
1.902
1.9
1.869
1.861
1.853
1.795
1968
1.945
1.944
1.896
1.894
1.888
1.834
1969
1.948
1.947
1.939
1.923
1.906
1.84
1970
1.943
1.943
1.943
1.936
1.926
1.875
1971
1.944
1.943
1.937
1.934
1.93
1.851
1972
1.944
1.943
1.939
1.936
1.932
1.861
1973
1.939
1.933
1.912
1.884
1.862
1.779
1974
1.88
1.879
1.878
1.875
1.858
1.755
1975
1.821
1.82
1.765
1.737
1.731
1.698
1976
1.904
1.903
1.848
1.817
1.814
1.782
1977
1.906
1.905
1.905
1.901
1.89
1.814
1978
1.887
1.886
1.882
1.686
1.509
1.224
1979
1.383
1.382
1.326
1.271
1.267
1.245
1980
1.452
1.451
1.395
1.365
1.356
1.32
1981
1.53
1.529
1.473
1.45
1.445
1.407
1982
1.563
1.562
1.526
1.525
1.52
1.461
1983
1.599
1.597
1.525
1.517
1.513
1.465
Sorted
results
Prob.
Peak
96
hr
21
Day
60
Day
90
Day
Yearly
0.027027027
1.948
1.947
1.943
1.936
1.932
1.875
0.054054054
1.945
1.944
1.939
1.936
1.93
1.861
0.081081081
1.944
1.943
1.939
1.934
1.926
1.851
0.108108108
1.944
1.943
1.937
1.923
1.906
1.84
0.135135135
1.943
1.943
1.912
1.901
1.89
1.834
0.162162162
1.939
1.933
1.905
1.894
1.888
1.814
0.189189189
1.906
1.905
1.896
1.884
1.862
1.795
0.216216216
1.904
1.903
1.882
1.875
1.858
1.782
0.243243243
1.902
1.9
1.878
1.861
1.853
1.779
0.27027027
1.887
1.886
1.869
1.817
1.814
1.755
0.297297297
1.88
1.879
1.848
1.781
1.765
1.715
0.324324324
1.821
1.82
1.801
1.737
1.731
1.698
0.351351351
1.821
1.808
1.765
1.686
1.626
1.569
0.378378378
1.81
1.764
1.636
1.633
1.562
1.509
0.405405405
1.64
1.639
1.584
1.567
1.536
1.508
0.432432432
1.599
1.597
1.577
1.539
1.52
1.465
0.459459459
1.584
1.582
1.574
1.525
1.513
1.461
0.486486486
1.578
1.577
1.526
1.517
1.509
1.445
0.513513514
1.574
1.574
1.525
1.517
1.482
1.417
0.540540541
1.563
1.562
1.521
1.493
1.47
1.417
0.567567568
1.551
1.55
1.495
1.473
1.459
1.407
0.594594595
1.545
1.544
1.494
1.463
1.456
1.356
0.621621622
1.53
1.529
1.488
1.45
1.445
1.355
0.648648649
1.504
1.502
1.473
1.444
1.441
1.342
0.675675676
1.496
1.496
1.439
1.367
1.364
1.32
0.702702703
1.452
1.451
1.395
1.365
1.356
1.294
0.72972973
1.383
1.382
1.342
1.34
1.337
1.245
0.756756757
1.363
1.362
1.326
1.271
1.267
1.224
0.783783784
1.346
1.345
1.289
1.231
1.227
1.206
0.810810811
1.236
1.235
1.179
1.111
1.108
1.085
0.837837838
0.9711
0.9705
0.9139
0.8359
0.8324
0.8194
0.864864865
0.8373
0.8327
0.7558
0.6753
0.6705
0.6532
0.891891892
0.6856
0.6837
0.6263
0.5467
0.5327
0.5219
0.918918919
0.5276
0.5273
0.47
0.3897
0.3751
0.3602
0.945945946
0.3617
0.3615
0.304
0.2228
0.2078
0.1896
20
0.972972973
0.1866
0.1865
0.1288
0.046620.03108
0.008098
0.1
1.944
1.943
1.9376
1.9263
1.912
1.8433
1.354899944
SCI­
GROW
output
file
SCIGROW
VERSION
2.1
MAY
1,
2001
RUN
No.
1
FOR
desmethyl
linuron
**
INPUT
VALUES
**
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­
APP
RATE
APPS/
TOTAL/
SOIL
AEROBIC
SOIL
METAB
(LBS/
AC)
YEAR
SEASON
KOC
HALFLIFE
(DAYS)
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­
.040
2
.080
208.0
99.00
GROUND­
WATER
SCREENING
CONCENTRATION
(IN
PPB)
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­
.0471
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

IR­
PCA
PRZM/
EXAMS
INPUT
FILE
FOR
THE
USE
OF
DESMETHOXY
LINURON
ON
CARROTS
IN
CALIFORNIA
WTR
WTR
***********************************
WTR
*
PESTICIDE
ROOT
ZONE
MODEL
*
WTR
*
RELEASE
3.12
Beta
*
WTR
*
February
1998
*

WTR
***********************************
WTR
WTR
***********************************
WTR
WTR
DEVELOPED
FOR:
WTR
U.
S.
ENVIRONMENTAL
PROTECTION
AGENCY
21
WTR
OFFICE
OF
RESEARCH
AND
DEVELOPMENT
WTR
NATIONAL
EXPOSURE
RESEARCH
LABORATORY
WTR
ECOSYSTEMS
RESEARCH
DIVISION
WTR
ATHENS,
GEORGIA
30605­
2700
WTR
706/
355­
8328
WTR
Distributed
by:
Des
Center
for
Exposure
Assessment
Modeling
WTR
http://
www.
epa.
gov/
CEAM
WTR
ceam@
epamail.
epa.
gov
WTR
WTR
WTR
WTR
SIMULATION
START
DATE
(DAY­
MONTH­
YEAR)
1
JAN.,
48
WTR
SIMULATION
END
DATE
(DAY­
MONTH­
YEAR)
31
DEC.,
83
WTR
WTR
WTR
"Lerdo
clay
loam,
MLRA
C­
17;
Central
Valley,
CA,
Carrots"
WTR
WTR
WTR
WTR
WTR
WTR
HYDROLOGY
AND
SEDIMENT
RELATED
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
PAN
COEFFICIENT
FOR
EVAPORATION
0.7000
WTR
FLAG
FOR
ET
SOURCE
(0=
EVAP,
1=
TEMP,
2=
EITHER)
0
WTR
DEPTH
TO
WHICH
ET
IS
COMPUTED
YEAR­
ROUND
(CM)
17.0000
WTR
SNOW
MELT
COEFFICIENT
(CM/
DEG­
C­
DAY)
0.5000
WTR
INITIAL
CROP
NUMBER
1
WTR
INITIAL
CROP
CONDITION
1
WTR
WTR
WTR
SOIL
EROSION
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
USLE
"K"
PARAMETER
0.2100
WTR
USLE
"LS"
PARAMETER
1.000
WTR
USLE
"P"
PARAMETER
1.000
WTR
FIELD
OR
PLOT
AREA
(HA)
172.0
WTR
STORM
TYPE
3
WTR
SLOPE
1.000
WTR
HYDRAULIC
LENGTH
(M)
600.0
WTR
WTR
WTR
CROPPING
EROSION
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
WTR
CROP
NUMBER
1
WTR
NUMBER
OF
USLEC
FACTORS
3
WTR
WTR
#
DAY
MONTH
USLEC
MANNINGS
N
WTR
WTR
1
1
1
0.100
0.020
WTR
2
21
9
0.100
0.000
WTR
3
22
9
0.100
*****
WTR
WTR
WTR
CROP
INFORMATION
WTR
­­­­­­­­­­­­­­­­
22
WTR
WTR
MAXIMUM
SURFACE
WTR
INTERCEPT.
MAXIMUM
MAXIMUM
MAXIMUM
CONDITION
MAXIMUM
WTR
CROP
POTENTIAL
ROOT
DEPTH
COVER
WEIGHT
AFTER
HEIGHT
AMC
RUNOFF
CURVE
NUMBERS
WTR
NUMBER
(CM)
(CM)
(%)
(KG/
M**
2)
HARVEST
(CM)
FALLOW
CROP
RESIDUE
WTR
WTR
I
80
70
75
WTR
1
0.2000
60.00
80.00
0.0000
3
100.000
II
91
85
88
WTR
III
96
93
95
WTR
WTR
WTR
CROP
ROTATION
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
CROP
EMERGENCE
MATURATION
HARVEST
WTR
NUMBER
DATE
DATE
DATE
WTR
WTR
1
10
SEP.,
49
23
DEC.,
49
31
DEC.,
48
WTR
1
10
SEP.,
50
23
DEC.,
50
31
DEC.,
49
WTR
1
10
SEP.,
51
23
DEC.,
51
31
DEC.,
50
WTR
1
10
SEP.,
52
23
DEC.,
52
31
DEC.,
51
WTR
1
10
SEP.,
53
23
DEC.,
53
31
DEC.,
52
WTR
1
10
SEP.,
54
23
DEC.,
54
31
DEC.,
53
WTR
1
10
SEP.,
55
23
DEC.,
55
31
DEC.,
54
WTR
1
10
SEP.,
56
23
DEC.,
56
31
DEC.,
55
WTR
1
10
SEP.,
57
23
DEC.,
57
31
DEC.,
56
WTR
1
10
SEP.,
58
23
DEC.,
58
31
DEC.,
57
WTR
1
10
SEP.,
59
23
DEC.,
59
31
DEC.,
58
WTR
1
10
SEP.,
60
23
DEC.,
60
31
DEC.,
59
WTR
1
10
SEP.,
61
23
DEC.,
61
31
DEC.,
60
WTR
1
10
SEP.,
62
23
DEC.,
62
31
DEC.,
61
WTR
1
10
SEP.,
63
23
DEC.,
63
31
DEC.,
62
WTR
1
10
SEP.,
64
23
DEC.,
64
31
DEC.,
63
WTR
1
10
SEP.,
65
23
DEC.,
65
31
DEC.,
64
WTR
1
10
SEP.,
66
23
DEC.,
66
31
DEC.,
65
WTR
1
10
SEP.,
67
23
DEC.,
67
31
DEC.,
66
WTR
1
10
SEP.,
68
23
DEC.,
68
31
DEC.,
67
WTR
1
10
SEP.,
69
23
DEC.,
69
31
DEC.,
68
WTR
1
10
SEP.,
70
23
DEC.,
70
31
DEC.,
69
WTR
1
10
SEP.,
71
23
DEC.,
71
31
DEC.,
70
WTR
1
10
SEP.,
72
23
DEC.,
72
31
DEC.,
71
WTR
1
10
SEP.,
73
23
DEC.,
73
31
DEC.,
72
WTR
1
10
SEP.,
74
23
DEC.,
74
31
DEC.,
73
WTR
1
10
SEP.,
75
23
DEC.,
75
31
DEC.,
74
WTR
1
10
SEP.,
76
23
DEC.,
76
31
DEC.,
75
WTR
1
10
SEP.,
77
23
DEC.,
77
31
DEC.,
76
WTR
1
10
SEP.,
78
23
DEC.,
78
31
DEC.,
77
WTR
1
10
SEP.,
79
23
DEC.,
79
31
DEC.,
78
WTR
1
10
SEP.,
80
23
DEC.,
80
31
DEC.,
79
WTR
1
10
SEP.,
81
23
DEC.,
81
31
DEC.,
80
WTR
1
10
SEP.,
82
23
DEC.,
82
31
DEC.,
81
WTR
1
10
SEP.,
83
23
DEC.,
83
31
DEC.,
82
WTR
1
10
SEP.,
84
23
DEC.,
84
31
DEC.,
83
WTR
WTR
WTR
desmethyl­
linuron
­
2
applications
@
0.04
kg/
ha
WTR
23
WTR
WTR
WTR
WTR
WTR
PESTICIDE
APPLICATION
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
CHEMICAL
PESTICIDE
INCORPORATION
WTR
PESICIDE
APPLICATION
APPLICATION
APPLIED
DEPTH
WTR
NAME
DATE
MODEL
(KG/
HA)
(CM)
WTR
WTR
desmethyl­
linuron
10
DEC.,
48
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
48
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
49
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
49
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
50
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
50
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
51
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
51
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
52
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
52
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
53
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
53
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
54
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
54
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
55
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
55
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
56
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
56
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
57
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
57
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
58
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
58
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
59
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
59
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
60
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
60
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
61
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
61
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
62
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
62
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
63
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
63
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
64
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
64
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
65
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
65
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
66
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
66
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
67
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
67
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
68
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
68
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
69
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
69
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
70
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
70
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
71
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
71
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
72
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
72
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
73
2
0.4000E­
01
0.0000
24
WTR
desmethyl­
linuron
24
DEC.,
73
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
74
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
74
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
75
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
75
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
76
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
76
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
77
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
77
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
78
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
78
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
79
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
79
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
80
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
80
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
81
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
81
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
82
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
82
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
10
DEC.,
83
2
0.4000E­
01
0.0000
WTR
desmethyl­
linuron
24
DEC.,
83
2
0.4000E­
01
0.0000
WTR
WTR
WTR
WTR
PLANT
PESTICIDE
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
WTR
FOLIAR
PESTICIDE
DECAY
RATE
(/
DAY)
0.0000
WTR
EXTRACTION
COEFFICIENT
(/
CM)
0.0000
WTR
FOLIAR
PESTICIDE
VOLATILIZATION
RATE
(/
DAY)
0.0000
WTR
FILTRATION
PARAMETER
(M**
2/
MG)
0.0000
WTR
AFTER
HARVEST
DATE,
REMAINING
CHEMICAL
1
IN
CANOPY
IS
SURFACE
APPLIED
WTR
PLANT
UPTAKE
EFFICIENCY
FACTOR
0.0000
WTR
WTR
WTR
Linuron
WTR
WTR
WTR
WTR
WTR
WTR
GENERAL
SOIL
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
CORE
DEPTH
(CM)
100.0
WTR
TOTAL
HORIZONS
IN
CORE
2
WTR
THETA
FLAG
(0=
INPUT,
1=
CALCULATED)
0
WTR
PARTITION
COEFFICIENT
FLAG
(0=
INPUT,
1=
CALCULATED)
1
WTR
BULK
DENSITY
FLAG
(0=
INPUT,
1=
CALCULATED)
0
WTR
SOIL
HYDRAULICS
MODULE
(0=
HYDR1,1=
HYDR2)
0
WTR
TRANSPORT
SOLUTION
TECHNIQUE
(0=
BACKDIFF,
1=
MOC)
0
WTR
IRRIGATION
FLAG
(0=
OFF,
1=
ON)
0
WTR
TEMPERATURE
CORRECTION
(0=
OFF,
1=
ON)
0
WTR
THERMAL
CONDUCTIVITY
(0=
SUPPLIED,
1=
CALCULATED)
0
WTR
BIODEGRADATION
FLAG
(0=
OFF,
1=
ON)
0
WTR
WTR
PESTICIDE
PROPERTY
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
HENRY'S
LAW
CONSTANT
0.0000
WTR
DIFFUSION
COEFFICIENT
(CM**
2/
DAY)
0.0000
WTR
25
WTR
WTR
WTR
WTR
SOIL
HORIZON
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
INITIAL
FIELD
WILTING
WTR
SOIL
CAPACITY
POINT
WTR
BULK
WATER
DRAINAGE
LAT
DRAIN
WATER
WATORGANIC
WTR
HORI­
THICK
DENSITY
CONTENT
PARAMETER
PARAMETER
CONTENT
CONTENT
CARBON
WTR
ZON
(CM)
(G/
CM**
3)
(CM/
CM)
(/
DAY)
(/
DAY)
(CM/
CM)
(CM/
CM)
(%)
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
1
18.0
1.6000
0.325
0.00
0.00
.32500
0.175
0.017
WTR
2
82.0
1.5000
0.249
0.00
0.00
.24900
0.129
0.002
WTR
WTR
WTR
HORIZON
LAYER
DEPTH
(CM)
WTR
WTR
1
1.00
WTR
2
1.00
WTR
WTR
desmethyl­
linuron
WTR
WTR
HORIZON
1
WTR
­­­­­­

WTR
WTR
LIQUID
PHASE
DECAY
RATE
(/
DAY)
0.700E­
02
WTR
SOLID
PHASE
DECAY
RATE
(/
DAY)
0.700E­
02
WTR
GAS
PHASE
DECAY
RATE
(/
DAY)
0.000
WTR
DISPERSION
COEFFICIENTS
(CM**
2/
DAY)
0.000
WTR
WTR
HORIZON
2
WTR
­­­­­­

WTR
WTR
LIQUID
PHASE
DECAY
RATE
(/
DAY)
0.700E­
02
WTR
SOLID
PHASE
DECAY
RATE
(/
DAY)
0.700E­
02
WTR
GAS
PHASE
DECAY
RATE
(/
DAY)
0.000
WTR
DISPERSION
COEFFICIENTS
(CM**
2/
DAY)
0.000
WTR
WTR
WTR
WTR
PLOT
FILE
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­

WTR
WTR
NUMBER
OF
PLOTTING
VARIABLES
7
WTR
TIMSER
NAME
MODE
CMPT
BEG
CMPT
END
CONSTANT
TYPE
DSN
WTR
WTR
PRCP
TCUM
0
0
0.0000
P
WTR
RUNF
TCUM
0
0
0.0000
P
WTR
INFL
TCUM
1
1
0.0000
P
WTR
ESLS
TCUM
0
0
1000.
P
WTR
RFLX
TCUM
0
0
0.1000E+
06
P
26
WTR
EFLX
TCUM
0
0
0.1000E+
06
P
WTR
RZFX
TCUM
0
0
0.1000E+
06
P
OUT
1948
12
31
24
0
0.0000
0.0000
0.0000
0.0000
OUT
1949
12
31
24
0
0.3138E­
05
0.4691E­
09
0.0000
0.0000
OUT
1950
12
31
24
0
0.4200E­
05
0.1769E­
08
0.0000
0.0000
OUT
1951
12
31
24
0
0.6374E­
05
0.3089E­
08
0.0000
0.0000
OUT
1952
12
31
24
0
0.5550E­
04
0.3689E­
07
0.0000
0.0000
OUT
1953
12
31
24
0
0.1085E­
05
0.4396E­
09
0.0000
0.0000
OUT
1954
12
31
24
0
0.1648E­
03
0.1314E­
06
0.0000
0.0000
OUT
1955
12
31
24
0
0.1462E­
04
0.7369E­
08
0.0000
0.0000
OUT
1956
12
31
24
0
0.5102E­
06
0.1537E­
09
0.0000
0.0000
OUT
1957
12
31
24
0
0.4680E­
04
0.3116E­
07
0.0000
0.0000
OUT
1958
12
31
24
0
0.5786E­
06
0.2378E­
09
0.0000
0.0000
OUT
1959
12
31
24
0
0.0000
0.0000
0.0000
0.0000
OUT
1960
12
31
24
0
0.3622E­
04
0.2090E­
07
0.0000
0.0000
OUT
1961
12
31
24
0
0.3295E­
08
0.9111E­
12
0.0000
0.0000
OUT
1962
12
31
24
0
0.1776E­
04
0.9296E­
08
0.2572E­
12
0.0000
OUT
1963
12
31
24
0
0.8455E­
04
0.5354E­
07
0.0000
0.0000
OUT
1964
12
31
24
0
0.3775E­
09
0.4864E­
13
0.0000
0.0000
OUT
1965
12
31
24
0
0.1799E­
03
0.1426E­
06
0.0000
0.0000
OUT
1966
12
31
24
0
0.6666E­
05
0.3252E­
08
0.0000
0.0000
OUT
1967
12
31
24
0
0.1010E­
03
0.7422E­
07
0.0000
0.0000
OUT
1968
12
31
24
0
0.3431E­
05
0.1375E­
08
0.0000
0.0000
OUT
1969
12
31
24
0
0.8540E­
06
0.3494E­
09
0.1875E­
10
0.0000
OUT
1970
12
31
24
0
0.1465E­
04
0.7266E­
08
0.0000
0.0000
OUT
1971
12
31
24
0
0.7705E­
06
0.3464E­
09
0.0000
0.0000
OUT
1972
12
31
24
0
0.3413E­
05
0.3211E­
08
0.0000
0.0000
OUT
1973
12
31
24
0
0.1987E­
04
0.1077E­
07
0.0000
0.0000
OUT
1974
12
31
24
0
0.8009E­
05
0.3416E­
08
0.0000
0.0000
OUT
1975
12
31
24
0
0.1499E­
04
0.8118E­
08
0.0000
0.0000
OUT
1976
12
31
24
0
0.1112E­
04
0.6433E­
08
0.0000
0.0000
OUT
1977
12
31
24
0
0.6883E­
04
0.4340E­
07
0.0000
0.0000
OUT
1978
12
31
24
0
0.2672E­
05
0.1322E­
08
0.9375E­
07
0.0000
OUT
1979
12
31
24
0
0.7743E­
05
0.3922E­
08
0.0000
0.0000
OUT
1980
12
31
24
0
0.4784E­
05
0.2111E­
08
0.0000
0.0000
OUT
1981
12
31
24
0
0.1599E­
04
0.9170E­
08
0.0000
0.0000
OUT
1982
12
31
24
0
0.9103E­
05
0.4244E­
08
0.0000
0.0000
OUT
1983
12
31
24
0
0.1430E­
03
0.9153E­
07
0.0000
0.0000
IR­
PCA
PRZM/
EXAMS
OUTPUT
FILE
FOR
THE
USE
OF
DESMETHOXY
LINURON
ON
CARROTS
IN
CALIFORNIA
27
Chemical:
desmethoxy­
linuron
PRZM
environment:
dsmthl1.
txt
EXAMS
environment:
IRPRZM0.
EXV
Metfile:
met17.
met
Water
segment
concentrations
(ppb)

Year
Peak
96
hr
21
Day
60
Day
90
Day
Yearly
1948
0.3728
0.3725
0.2571
0.09312
0.06208
0.01617
1949
0.7207
0.72
0.6054
0.4439
0.4141
0.3781
1950
1.048
1.047
0.9335
0.7744
0.7457
0.7165
1951
1.358
1.354
1.241
1.084
1.056
1.035
1952
1.656
1.646
1.495
1.337
1.328
1.293
1953
1.917
1.915
1.803
1.65
1.645
1.619
1954
2.438
2.435
2.324
2.196
2.189
2.142
1955
2.646
2.643
2.533
2.425
2.417
2.374
1956
2.673
2.67
2.635
2.632
2.626
2.539
1957
2.944
2.939
2.816
2.677
2.672
2.629
1958
2.925
2.925
2.924
2.918
2.897
2.651
1959
3.023
3.02
2.91
2.817
2.811
2.763
1960
3.085
3.082
3.072
3.053
3.043
2.937
1961
3.067
3.064
2.954
2.864
2.858
2.809
1962
3.055
3.055
3.054
2.945
2.831
2.63
1963
3.001
2.998
2.888
2.838
2.826
2.752
1964
3.18
3.177
3.068
2.985
2.978
2.926
1965
3.536
3.423
3.167
3.163
3.149
3.037
1966
3.513
3.51
3.496
3.457
3.426
3.327
1967
3.688
3.684
3.628
3.613
3.597
3.483
1968
3.764
3.761
3.673
3.668
3.656
3.551
1969
3.762
3.758
3.747
3.716
3.683
3.555
1970
3.747
3.747
3.747
3.734
3.715
3.615
1971
3.743
3.739
3.73
3.725
3.717
3.563
1972
3.738
3.735
3.728
3.723
3.715
3.578
1973
3.724
3.712
3.671
3.619
3.577
3.415
1974
3.607
3.607
3.604
3.598
3.565
3.368
1975
3.495
3.492
3.383
3.331
3.32
3.256
1976
3.651
3.648
3.54
3.484
3.478
3.416
1977
3.65
3.65
3.648
3.642
3.621
3.473
1978
3.617
3.615
3.607
3.233
2.894
2.346
1979
2.66
2.657
2.547
2.439
2.432
2.389
1980
2.793
2.791
2.68
2.622
2.604
2.536
1981
2.944
2.941
2.832
2.787
2.777
2.703
1982
3.006
3.004
2.933
2.931
2.921
2.808
1983
3.087
3.081
2.939
2.923
2.914
2.821
Sorted
results
Prob.
Peak
96
hr
21
Day
60
Day
90
Day
Yearly
0.027027027
3.764
3.761
3.747
3.734
3.717
3.615
0.054054054
3.762
3.758
3.747
3.725
3.715
3.578
0.081081081
3.747
3.747
3.73
3.723
3.715
3.563
0.108108108
3.743
3.739
3.728
3.716
3.683
3.555
0.135135135
3.738
3.735
3.673
3.668
3.656
3.551
0.162162162
3.724
3.712
3.671
3.642
3.621
3.483
0.189189189
3.688
3.684
3.648
3.619
3.597
3.473
0.216216216
3.651
3.65
3.628
3.613
3.577
3.416
0.243243243
3.65
3.648
3.607
3.598
3.565
3.415
0.27027027
3.617
3.615
3.604
3.484
3.478
3.368
0.297297297
3.607
3.607
3.54
3.457
3.426
3.327
0.324324324
3.536
3.51
3.496
3.331
3.32
3.256
0.351351351
3.513
3.492
3.383
3.233
3.149
3.037
0.378378378
3.495
3.423
3.167
3.163
3.043
2.937
0.405405405
3.18
3.177
3.072
3.053
2.978
2.926
28
0.432432432
3.087
3.082
3.068
2.985
2.921
2.821
0.459459459
3.085
3.081
3.054
2.945
2.914
2.809
0.486486486
3.067
3.064
2.954
2.931
2.897
2.808
0.513513514
3.055
3.055
2.939
2.923
2.894
2.763
0.540540541
3.023
3.02
2.933
2.918
2.858
2.752
0.567567568
3.006
3.004
2.924
2.864
2.831
2.703
0.594594595
3.001
2.998
2.91
2.838
2.826
2.651
0.621621622
2.944
2.941
2.888
2.817
2.811
2.63
0.648648649
2.944
2.939
2.832
2.787
2.777
2.629
0.675675676
2.925
2.925
2.816
2.677
2.672
2.539
0.702702703
2.793
2.791
2.68
2.632
2.626
2.536
0.72972973
2.673
2.67
2.635
2.622
2.604
2.389
0.756756757
2.66
2.657
2.547
2.439
2.432
2.374
0.783783784
2.646
2.643
2.533
2.425
2.417
2.346
0.810810811
2.438
2.435
2.324
2.196
2.189
2.142
0.837837838
1.917
1.915
1.803
1.65
1.645
1.619
0.864864865
1.656
1.646
1.495
1.337
1.328
1.293
0.891891892
1.358
1.354
1.241
1.084
1.056
1.035
0.918918919
1.048
1.047
0.9335
0.7744
0.7457
0.7165
0.945945946
0.7207
0.72
0.6054
0.4439
0.4141
0.3781
0.972972973
0.3728
0.3725
0.2571
0.09312
0.06208
0.01617
0.1
3.7442
3.7414
3.7286
3.7181
3.6926
3.5574
2.623604722
SCI­
GROW
output
file
SCIGROW
VERSION
2.1
MAY
1,
2001
RUN
No.
1
FOR
desmethoxy
linuron
**
INPUT
VALUES
**
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

­­­
APP
RATE
APPS/
TOTAL/
SOIL
AEROBIC
SOIL
METAB
(LBS/
AC)
YEAR
SEASON
KOC
HALFLIFE
(DAYS)
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

­­­
.080
2
.160
208.0
99.00
GROUND­
WATER
SCREENING
CONCENTRATION
(IN
PPB)
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­
.0942
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­
29
IR­
PCA
PRZM/
EXAMS
INPUT
FILE
FOR
THE
USE
OF
NOR
LINURON
ON
CARROTS
IN
CALIFORNIA
WTR
WTR
***********************************
WTR
*
PESTICIDE
ROOT
ZONE
MODEL
*
WTR
*
RELEASE
3.12
Beta
*
WTR
*
February
1998
*
WTR
***********************************
WTR
WTR
***********************************
WTR
WTR
DEVELOPED
FOR:
WTR
U.
S.
ENVIRONMENTAL
PROTECTION
AGENCY
WTR
OFFICE
OF
RESEARCH
AND
DEVELOPMENT
WTR
NATIONAL
EXPOSURE
RESEARCH
LABORATORY
WTR
ECOSYSTEMS
RESEARCH
DIVISION
WTR
ATHENS,
GEORGIA
30605­
2700
WTR
706/
355­
8328
WTR
Distributed
by:
Des
Center
for
Exposure
Assessment
Modeling
WTR
http://
www.
epa.
gov/
CEAM
WTR
ceam@
epamail.
epa.
gov
WTR
WTR
WTR
WTR
SIMULATION
START
DATE
(DAY­
MONTH­
YEAR)
1
JAN.,
48
WTR
SIMULATION
END
DATE
(DAY­
MONTH­
YEAR)
31
DEC.,
83
WTR
WTR
WTR
"Lerdo
clay
loam,
MLRA
C­
17;
Central
Valley,
CA,
Carrots"
WTR
WTR
WTR
WTR
WTR
WTR
HYDROLOGY
AND
SEDIMENT
RELATED
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
PAN
COEFFICIENT
FOR
EVAPORATION
0.7000
WTR
FLAG
FOR
ET
SOURCE
(0=
EVAP,
1=
TEMP,
2=
EITHER)
0
30
WTR
DEPTH
TO
WHICH
ET
IS
COMPUTED
YEAR­
ROUND
(CM)
17.0000
WTR
SNOW
MELT
COEFFICIENT
(CM/
DEG­
C­
DAY)
0.5000
WTR
INITIAL
CROP
NUMBER
1
WTR
INITIAL
CROP
CONDITION
1
WTR
WTR
WTR
SOIL
EROSION
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
USLE
"K"
PARAMETER
0.2100
WTR
USLE
"LS"
PARAMETER
1.000
WTR
USLE
"P"
PARAMETER
1.000
WTR
FIELD
OR
PLOT
AREA
(HA)
172.0
WTR
STORM
TYPE
3
WTR
SLOPE
1.000
WTR
HYDRAULIC
LENGTH
(M)
600.0
WTR
WTR
WTR
CROPPING
EROSION
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
WTR
CROP
NUMBER
1
WTR
NUMBER
OF
USLEC
FACTORS
3
WTR
WTR
#
DAY
MONTH
USLEC
MANNINGS
N
WTR
WTR
1
1
1
0.100
0.020
WTR
2
21
9
0.100
0.000
WTR
3
22
9
0.100
*****
WTR
WTR
WTR
CROP
INFORMATION
WTR
­­­­­­­­­­­­­­­

WTR
WTR
MAXIMUM
SURFACE
WTR
INTERCEPT.
MAXIMUM
MAXIMUM
MAXIMUM
CONDITION
MAXIMUM
WTR
CROP
POTENTIAL
ROOT
DEPTH
COVER
WEIGHT
AFTER
HEIGHT
AMC
RUNOFF
CURVE
NUMBERS
WTR
NUMBER
(CM)
(CM)
(%)
(KG/
M**
2)
HARVEST
(CM)
FALLOW
CROP
RESIDUE
WTR
WTR
I
80
70
75
WTR
1
0.2000
60.00
80.00
0.0000
3
100.000
II
91
85
88
WTR
III
96
93
95
WTR
WTR
WTR
CROP
ROTATION
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
CROP
EMERGENCE
MATURATION
HARVEST
WTR
NUMBER
DATE
DATE
DATE
WTR
WTR
1
10
SEP.,
49
23
DEC.,
49
31
DEC.,
48
WTR
1
10
SEP.,
50
23
DEC.,
50
31
DEC.,
49
WTR
1
10
SEP.,
51
23
DEC.,
51
31
DEC.,
50
WTR
1
10
SEP.,
52
23
DEC.,
52
31
DEC.,
51
WTR
1
10
SEP.,
53
23
DEC.,
53
31
DEC.,
52
WTR
1
10
SEP.,
54
23
DEC.,
54
31
DEC.,
53
31
WTR
1
10
SEP.,
55
23
DEC.,
55
31
DEC.,
54
WTR
1
10
SEP.,
56
23
DEC.,
56
31
DEC.,
55
WTR
1
10
SEP.,
57
23
DEC.,
57
31
DEC.,
56
WTR
1
10
SEP.,
58
23
DEC.,
58
31
DEC.,
57
WTR
1
10
SEP.,
59
23
DEC.,
59
31
DEC.,
58
WTR
1
10
SEP.,
60
23
DEC.,
60
31
DEC.,
59
WTR
1
10
SEP.,
61
23
DEC.,
61
31
DEC.,
60
WTR
1
10
SEP.,
62
23
DEC.,
62
31
DEC.,
61
WTR
1
10
SEP.,
63
23
DEC.,
63
31
DEC.,
62
WTR
1
10
SEP.,
64
23
DEC.,
64
31
DEC.,
63
WTR
1
10
SEP.,
65
23
DEC.,
65
31
DEC.,
64
WTR
1
10
SEP.,
66
23
DEC.,
66
31
DEC.,
65
WTR
1
10
SEP.,
67
23
DEC.,
67
31
DEC.,
66
WTR
1
10
SEP.,
68
23
DEC.,
68
31
DEC.,
67
WTR
1
10
SEP.,
69
23
DEC.,
69
31
DEC.,
68
WTR
1
10
SEP.,
70
23
DEC.,
70
31
DEC.,
69
WTR
1
10
SEP.,
71
23
DEC.,
71
31
DEC.,
70
WTR
1
10
SEP.,
72
23
DEC.,
72
31
DEC.,
71
WTR
1
10
SEP.,
73
23
DEC.,
73
31
DEC.,
72
WTR
1
10
SEP.,
74
23
DEC.,
74
31
DEC.,
73
WTR
1
10
SEP.,
75
23
DEC.,
75
31
DEC.,
74
WTR
1
10
SEP.,
76
23
DEC.,
76
31
DEC.,
75
WTR
1
10
SEP.,
77
23
DEC.,
77
31
DEC.,
76
WTR
1
10
SEP.,
78
23
DEC.,
78
31
DEC.,
77
WTR
1
10
SEP.,
79
23
DEC.,
79
31
DEC.,
78
WTR
1
10
SEP.,
80
23
DEC.,
80
31
DEC.,
79
WTR
1
10
SEP.,
81
23
DEC.,
81
31
DEC.,
80
WTR
1
10
SEP.,
82
23
DEC.,
82
31
DEC.,
81
WTR
1
10
SEP.,
83
23
DEC.,
83
31
DEC.,
82
WTR
1
10
SEP.,
84
23
DEC.,
84
31
DEC.,
83
WTR
WTR
WTR
nor­
linuron
­
2
applications
@
0.03
kg/
ha
WTR
WTR
WTR
WTR
WTR
WTR
PESTICIDE
APPLICATION
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
CHEMICAL
PESTICIDE
INCORPORATION
WTR
PESICIDE
APPLICATION
APPLICATION
APPLIED
DEPTH
WTR
NAME
DATE
MODEL
(KG/
HA)
(CM)
WTR
WTR
nor­
linuron
10
DEC.,
48
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
48
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
49
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
49
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
50
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
50
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
51
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
51
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
52
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
52
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
53
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
53
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
54
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
54
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
55
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
55
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
56
2
0.3000E­
01
0.0000
32
WTR
nor­
linuron
24
DEC.,
56
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
57
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
57
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
58
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
58
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
59
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
59
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
60
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
60
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
61
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
61
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
62
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
62
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
63
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
63
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
64
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
64
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
65
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
65
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
66
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
66
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
67
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
67
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
68
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
68
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
69
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
69
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
70
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
70
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
71
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
71
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
72
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
72
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
73
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
73
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
74
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
74
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
75
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
75
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
76
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
76
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
77
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
77
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
78
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
78
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
79
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
79
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
80
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
80
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
81
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
81
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
82
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
82
2
0.3000E­
01
0.0000
WTR
nor­
linuron
10
DEC.,
83
2
0.3000E­
01
0.0000
WTR
nor­
linuron
24
DEC.,
83
2
0.3000E­
01
0.0000
WTR
WTR
WTR
WTR
PLANT
PESTICIDE
PARAMETERS
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
33
WTR
FOLIAR
PESTICIDE
DECAY
RATE
(/
DAY)
0.0000
WTR
EXTRACTION
COEFFICIENT
(/
CM)
0.0000
WTR
FOLIAR
PESTICIDE
VOLATILIZATION
RATE
(/
DAY)
0.0000
WTR
FILTRATION
PARAMETER
(M**
2/
MG)
0.0000
WTR
AFTER
HARVEST
DATE,
REMAINING
CHEMICAL
1
IN
CANOPY
IS
SURFACE
APPLIED
WTR
PLANT
UPTAKE
EFFICIENCY
FACTOR
0.0000
WTR
WTR
WTR
Linuron
WTR
WTR
WTR
WTR
WTR
WTR
GENERAL
SOIL
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
CORE
DEPTH
(CM)
100.0
WTR
TOTAL
HORIZONS
IN
CORE
2
WTR
THETA
FLAG
(0=
INPUT,
1=
CALCULATED)
0
WTR
PARTITION
COEFFICIENT
FLAG
(0=
INPUT,
1=
CALCULATED)
1
WTR
BULK
DENSITY
FLAG
(0=
INPUT,
1=
CALCULATED)
0
WTR
SOIL
HYDRAULICS
MODULE
(0=
HYDR1,1=
HYDR2)
0
WTR
TRANSPORT
SOLUTION
TECHNIQUE
(0=
BACKDIFF,
1=
MOC)
0
WTR
IRRIGATION
FLAG
(0=
OFF,
1=
ON)
0
WTR
TEMPERATURE
CORRECTION
(0=
OFF,
1=
ON)
0
WTR
THERMAL
CONDUCTIVITY
(0=
SUPPLIED,
1=
CALCULATED)
0
WTR
BIODEGRADATION
FLAG
(0=
OFF,
1=
ON)
0
WTR
WTR
PESTICIDE
PROPERTY
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
HENRY'S
LAW
CONSTANT
0.0000
WTR
DIFFUSION
COEFFICIENT
(CM**
2/
DAY)
0.0000
WTR
WTR
WTR
WTR
WTR
SOIL
HORIZON
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
INITIAL
FIELD
WILTING
WTR
SOIL
CAPACITY
POINT
WTR
BULK
WATER
DRAINAGE
LAT
DRAIN
WATER
WATORGANIC
WTR
HORI­
THICK
DENSITY
CONTENT
PARAMETER
PARAMETER
CONTENT
CONTENT
CARBON
WTR
ZON
(CM)
(G/
CM**
3)
(CM/
CM)
(/
DAY)
(/
DAY)
(CM/
CM)
(CM/
CM)
(%)

WTR
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

­­­­­­­­­­­­­­­­­­­­­­­­­­­­­

WTR
WTR
1
18.0
1.6000
0.325
0.00
0.00
.32500
0.175
0.017
WTR
2
82.0
1.5000
0.249
0.00
0.00
.24900
0.129
0.002
WTR
WTR
WTR
HORIZON
LAYER
DEPTH
(CM)
WTR
34
WTR
1
1.00
WTR
2
1.00
WTR
WTR
nor­
linuron
WTR
WTR
HORIZON
1
WTR
­­­­­­

WTR
WTR
LIQUID
PHASE
DECAY
RATE
(/
DAY)
0.700E­
02
WTR
SOLID
PHASE
DECAY
RATE
(/
DAY)
0.700E­
02
WTR
GAS
PHASE
DECAY
RATE
(/
DAY)
0.000
WTR
DISPERSION
COEFFICIENTS
(CM**
2/
DAY)
0.000
WTR
WTR
HORIZON
2
WTR
­­­­­­

WTR
WTR
LIQUID
PHASE
DECAY
RATE
(/
DAY)
0.700E­
02
WTR
SOLID
PHASE
DECAY
RATE
(/
DAY)
0.700E­
02
WTR
GAS
PHASE
DECAY
RATE
(/
DAY)
0.000
WTR
DISPERSION
COEFFICIENTS
(CM**
2/
DAY)
0.000
WTR
WTR
WTR
WTR
PLOT
FILE
INFORMATION
WTR
­­­­­­­­­­­­­­­­­­­­

WTR
WTR
NUMBER
OF
PLOTTING
VARIABLES
7
WTR
TIMSER
NAME
MODE
CMPT
BEG
CMPT
END
CONSTANT
TYPE
DSN
WTR
WTR
PRCP
TCUM
0
0
0.0000
P
WTR
RUNF
TCUM
0
0
0.0000
P
WTR
INFL
TCUM
1
1
0.0000
P
WTR
ESLS
TCUM
0
0
1000.
P
WTR
RFLX
TCUM
0
0
0.1000E+
06
P
WTR
EFLX
TCUM
0
0
0.1000E+
06
P
WTR
RZFX
TCUM
0
0
0.1000E+
06
P
OUT
1948
12
31
24
0
0.0000
0.0000
0.0000
0.0000
OUT
1949
12
31
24
0
0.2354E­
05
0.3518E­
09
0.0000
0.0000
OUT
1950
12
31
24
0
0.3150E­
05
0.1327E­
08
0.0000
0.0000
OUT
1951
12
31
24
0
0.4780E­
05
0.2317E­
08
0.0000
0.0000
OUT
1952
12
31
24
0
0.4163E­
04
0.2767E­
07
0.0000
0.0000
OUT
1953
12
31
24
0
0.8135E­
06
0.3297E­
09
0.0000
0.0000
OUT
1954
12
31
24
0
0.1236E­
03
0.9855E­
07
0.0000
0.0000
OUT
1955
12
31
24
0
0.1096E­
04
0.5526E­
08
0.0000
0.0000
OUT
1956
12
31
24
0
0.3827E­
06
0.1153E­
09
0.0000
0.0000
OUT
1957
12
31
24
0
0.3510E­
04
0.2337E­
07
0.0000
0.0000
OUT
1958
12
31
24
0
0.4340E­
06
0.1784E­
09
0.0000
0.0000
OUT
1959
12
31
24
0
0.0000
0.0000
0.0000
0.0000
OUT
1960
12
31
24
0
0.2717E­
04
0.1567E­
07
0.0000
0.0000
OUT
1961
12
31
24
0
0.2471E­
08
0.6833E­
12
0.0000
0.0000
OUT
1962
12
31
24
0
0.1332E­
04
0.6972E­
08
0.1929E­
12
0.0000
OUT
1963
12
31
24
0
0.6341E­
04
0.4015E­
07
0.0000
0.0000
OUT
1964
12
31
24
0
0.2831E­
09
0.3648E­
13
0.0000
0.0000
OUT
1965
12
31
24
0
0.1349E­
03
0.1069E­
06
0.0000
0.0000
OUT
1966
12
31
24
0
0.5000E­
05
0.2439E­
08
0.0000
0.0000
OUT
1967
12
31
24
0
0.7577E­
04
0.5567E­
07
0.0000
0.0000
OUT
1968
12
31
24
0
0.2573E­
05
0.1032E­
08
0.0000
0.0000
OUT
1969
12
31
24
0
0.6405E­
06
0.2620E­
09
0.1407E­
10
0.0000
OUT
1970
12
31
24
0
0.1098E­
04
0.5450E­
08
0.0000
0.0000
OUT
1971
12
31
24
0
0.5779E­
06
0.2598E­
09
0.0000
0.0000
OUT
1972
12
31
24
0
0.2560E­
05
0.2408E­
08
0.0000
0.0000
OUT
1973
12
31
24
0
0.1490E­
04
0.8077E­
08
0.0000
0.0000
35
OUT
1974
12
31
24
0
0.6007E­
05
0.2562E­
08
0.0000
0.0000
OUT
1975
12
31
24
0
0.1125E­
04
0.6089E­
08
0.0000
0.0000
OUT
1976
12
31
24
0
0.8344E­
05
0.4824E­
08
0.0000
0.0000
OUT
1977
12
31
24
0
0.5162E­
04
0.3255E­
07
0.0000
0.0000
OUT
1978
12
31
24
0
0.2004E­
05
0.9915E­
09
0.7032E­
07
0.0000
OUT
1979
12
31
24
0
0.5807E­
05
0.2942E­
08
0.0000
0.0000
OUT
1980
12
31
24
0
0.3588E­
05
0.1583E­
08
0.0000
0.0000
OUT
1981
12
31
24
0
0.1199E­
04
0.6877E­
08
0.0000
0.0000
OUT
1982
12
31
24
0
0.6827E­
05
0.3183E­
08
0.0000
0.0000
OUT
1983
12
31
24
0
0.1073E­
03
0.6865E­
07
0.0000
0.0000
IR­
PCA
PRZM/
EXAMS
OUTPUT
FILE
FOR
THE
USE
OF
NOR
LINURON
ON
CARROTS
IN
CALIFORNIA
Chemical:
nor­
linuron
PRZM
environment:
dsmthl1.
txt
EXAMS
environment:
IRPRZM0.
EXV
Metfile:
met17.
met
Water
segment
concentrations
(ppb)

Year
Peak
96
hr
21
Day
60
Day
90
Day
Yearly
1948
0.14
0.1399
0.0966
0.03498
0.02332
0.006075
1949
0.2713
0.2711
0.228
0.167
0.1557
0.1421
1950
0.3956
0.3954
0.3524
0.292
0.2811
0.27
1951
0.514
0.5127
0.4694
0.4096
0.399
0.3912
1952
0.6277
0.6242
0.5664
0.5064
0.5027
0.4894
1953
0.7277
0.7273
0.6847
0.626
0.624
0.6139
1954
0.9261
0.9256
0.8833
0.833
0.8303
0.8126
1955
1.008
1.007
0.965
0.9224
0.9193
0.903
1956
1.021
1.02
1.005
1.004
1.002
0.9685
1957
1.126
1.124
1.077
1.023
1.021
1.005
1958
1.12
1.12
1.12
1.118
1.109
1.015
1959
1.161
1.16
1.118
1.081
1.079
1.06
1960
1.186
1.185
1.181
1.173
1.169
1.129
1961
1.181
1.18
1.138
1.103
1.1
1.081
1962
1.178
1.178
1.178
1.135
1.092
1.013
1963
1.156
1.155
1.113
1.095
1.09
1.06
1964
1.227
1.226
1.184
1.152
1.149
1.129
1965
1.363
1.32
1.224
1.222
1.217
1.173
1966
1.354
1.353
1.348
1.333
1.321
1.282
1967
1.423
1.422
1.399
1.393
1.387
1.343
1968
1.455
1.454
1.419
1.417
1.412
1.371
1969
1.457
1.456
1.451
1.438
1.426
1.376
1970
1.453
1.453
1.453
1.448
1.44
1.401
1971
1.453
1.453
1.449
1.447
1.443
1.383
36
1972
1.453
1.453
1.45
1.448
1.445
1.391
1973
1.45
1.445
1.429
1.409
1.392
1.329
1974
1.405
1.405
1.404
1.402
1.389
1.312
1975
1.361
1.361
1.319
1.298
1.294
1.268
1976
1.423
1.422
1.381
1.359
1.356
1.332
1977
1.425
1.424
1.424
1.421
1.413
1.355
1978
1.41
1.41
1.407
1.261
1.128
0.9146
1979
1.034
1.033
0.991
0.9499
0.9469
0.93
1980
1.085
1.085
1.043
1.021
1.014
0.9867
1981
1.144
1.143
1.101
1.084
1.08
1.051
1982
1.168
1.168
1.141
1.14
1.136
1.092
1983
1.196
1.194
1.141
1.135
1.132
1.095
Sorted
results
Prob.
Peak
96
hr
21
Day
60
Day
90
Day
Yearly
0.027027027
1.457
1.456
1.453
1.448
1.445
1.401
0.054054054
1.455
1.454
1.451
1.448
1.443
1.391
0.081081081
1.453
1.453
1.45
1.447
1.44
1.383
0.108108108
1.453
1.453
1.449
1.438
1.426
1.376
0.135135135
1.453
1.453
1.429
1.421
1.413
1.371
0.162162162
1.45
1.445
1.424
1.417
1.412
1.355
0.189189189
1.425
1.424
1.419
1.409
1.392
1.343
0.216216216
1.423
1.422
1.407
1.402
1.389
1.332
0.243243243
1.423
1.422
1.404
1.393
1.387
1.329
0.27027027
1.41
1.41
1.399
1.359
1.356
1.312
0.297297297
1.405
1.405
1.381
1.333
1.321
1.282
0.324324324
1.363
1.361
1.348
1.298
1.294
1.268
0.351351351
1.361
1.353
1.319
1.261
1.217
1.173
0.378378378
1.354
1.32
1.224
1.222
1.169
1.129
0.405405405
1.227
1.226
1.184
1.173
1.149
1.129
0.432432432
1.196
1.194
1.181
1.152
1.136
1.095
0.459459459
1.186
1.185
1.178
1.14
1.132
1.092
0.486486486
1.181
1.18
1.141
1.135
1.128
1.081
0.513513514
1.178
1.178
1.141
1.135
1.109
1.06
0.540540541
1.168
1.168
1.138
1.118
1.1
1.06
0.567567568
1.161
1.16
1.12
1.103
1.092
1.051
0.594594595
1.156
1.155
1.118
1.095
1.09
1.015
0.621621622
1.144
1.143
1.113
1.084
1.08
1.013
0.648648649
1.126
1.124
1.101
1.081
1.079
1.005
0.675675676
1.12
1.12
1.077
1.023
1.021
0.9867
0.702702703
1.085
1.085
1.043
1.021
1.014
0.9685
0.72972973
1.034
1.033
1.005
1.004
1.002
0.93
0.756756757
1.021
1.02
0.991
0.9499
0.9469
0.9146
0.783783784
1.008
1.007
0.965
0.9224
0.9193
0.903
0.810810811
0.9261
0.9256
0.8833
0.833
0.8303
0.8126
0.837837838
0.7277
0.7273
0.6847
0.626
0.624
0.6139
0.864864865
0.6277
0.6242
0.5664
0.5064
0.5027
0.4894
0.891891892
0.514
0.5127
0.4694
0.4096
0.399
0.3912
0.918918919
0.3956
0.3954
0.3524
0.292
0.2811
0.27
0.945945946
0.2713
0.2711
0.228
0.167
0.1557
0.1421
0.972972973
0.14
0.1399
0.0966
0.034980.02332
0.006075
0.1
1.453
1.453
1.4493
1.4407
1.4302
1.3781
1.01316875
37
SCI­
GROW
output
file
SCIGROW
VERSION
2.1
MAY
1,
2001
RUN
No.
1
FOR
nor
linuron
**
INPUT
VALUES
**
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­
APP
RATE
APPS/
TOTAL/
SOIL
AEROBIC
SOIL
METAB
(LBS/
AC)
YEAR
SEASON
KOC
HALFLIFE
(DAYS)
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­
.030
2
.060
208.0
99.00
GROUND­
WATER
SCREENING
CONCENTRATION
(IN
PPB)
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­
.0353
­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­­
38