Worksheet A07b [KPMODEL]: Estimate of dermal permeability (K
p
in cm/hr) and 95%
confidence
intervals (data from U.S. EPA/ORD 1992).
Model parameters
ID
Value
Coefficient for k
o/w
C_KOW
0.706648
Coefficient for MW
C_MW
0.006151
Model Constant
C
2.72576
Number of data points
DP
90
Degrees of Freedom (d.f.)
DF
87
Critical value of
t
0.025
with 87 d.f.
1
CRIT
1.96
Standard
error of the estimate
SEE
45.9983
Mean square error or model variance
MDLV
0.528716
Standard deviation of model (s)
MSD
0.727129
MDLV
0.5
X
N
X, cross products matrix
0.0550931
-0.0000941546
-0.0103443
-0.0000941546
0.0000005978
-0.0000222508
-0.0103443
-0.0000222508
0.00740677
1
Mendenhall and Scheaffer, 1973, Appendix 3, Table 4, p. A31.
NOTE: The data for this analysis is taken from U.S. EPA/ORD (1992), Dermal Exposure Assessment: Principles
and
Applications, EPA/600/8-91/011B, Table 5-4, pp. 5-15 through 5-19. The EPA report, however, does not
provide sufficient information for the calculation of confidence intervals. The synopsis of the above analysis was
conducted in STATGRAPHICS Plus for Windows, Version 3.1 (Manugistics, 1995)
as well as Mathematica,
Version 3.0.1.1 (Wolfram Research, 1997). Although not explicitly stated in the EPA report, 3 of the 93 data
points are censored from the analysis because they are statistical outliers: [Hydrocortisone-21-yl]-hemipimelate, n
nonanol, and n-propanol. The model parameters reported above are consistent with those reported by U.S. EPA
but are carried out to greater number of decimal places to reduce rounding errors when calculating the confidence
intervals. See notes to Worksheet A07a for details of calculating maximum likelihood estimates and confidence
intervals.
WS-12
CHEMICAL SPECIFIC VALUES
Worksheet B01 [APPL]
: Anticipated Application and Dilution Rates for sethoxydim
Item
Code
Value
Units
Source
Application rate (
R)
Central
Typ
0.3
lb/acre
Section 2.4
Lower
Low
0.09375
Section 2.4
Upper
Hi
0.375
Section 2.4
Dilution (
Dil)
Central
CDil
10
gal./acre
Section 2.4
Lower
LDil
5
Upper
HDil
20
Concentration in field solutions
1
:
R
(lb/acre)
÷ Dil
(gal/acre)
× 119.8 mg/mL÷lb/gal
Central
TypDr
3.6
0.56
9
mg/mL
Lower
LowDr
Upper
HI_Dr
The typical concentration in applied solution is calculated as the typical application rate (lbs/acre) divided by
the typical dilution (gal/acre), yielding units of lbs/gallon. This is converted to mg/mL using the relationship of
lb/gal = 119.8 mg/mL from Worksheet A01. The lowest estimated concentration
is calculated as the lowest
application rate divided by the highest dilution. The highest estimated concentration is calculated as highest
application rate divided by the lowest dilution.
NOTE ON UNITS FOR APPLICATION RATE: In all cases, lb/acre refers to
lb a.i./acre.
WS-13
Worksheet B02 [CHEM]
: Summary of chemical specific values used for sethoxydim in exposure assessment
worksheets.
Parameter
ID
Value
Units
Source/Reference
Molecular
weight
MW
327.50
grams/mole
Table 2-1
Water Solubility, pH 7 and 20°C
WS
4700
mg/L
Table 2-1
K
o/w
, pH 7
Kow
45.1
unitless
Table 2.1, log K
o/w
= 1.65
Foliar half-time ( t
½
)
FT12
3
days
Table 2-1
central
FrT12C
3
days
lower
FrT12L
3
days
upper
FrT12U
3
days
Dissipation coefficients on vegetation
central
VgKC
0.231049
day
-1
ln(2)/half-time.
The upper limit on half-
lower
VgKL
0.231049
day
-1
time is used to calculate
the
lower limit on
upper
VgKU
0.231049
day
-1
dissipation coefficient.
Bioconcentration factor, edible
BCFT
1.2
L/kg fish
Section 3.2.3.5.
portion, acute exposure
Bioconcentration factor, edible
BCFCh
7
L/kg fish
portion, chronic exposure
Bioconcentration factor,
whole fish,
BCFWA
3.6
L/kg fish
acute
Bioconcentration factor, whole fish,
BCFWC
21
L/kg fish
chronic
Chronic RfD
a
RfDP
0.09
mg/kg bw/day
Section 3.3.3
Acute RfD
RfDA
0.6
mg/kg bw/day
Section 3.3.3
WS-14