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&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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                    <text>Item ID Number

°0979

Author

Ramsey, J. C.

Corporate Author
Report/Article Title Exposure of Forest Workers to 2,4,5-T: Calculated
Dose Levels

Journal/Book Title
Year

1979

Month/Day

March

Color
Number of Images

n

33

Alvin L. Young filed this item under the category
"Human Exposure to Phenoxy Herbicides and TCDD"

Friday, March 30, 2001

Page 979 of 1070

�ALVIN L YOUNG, Major, USAF
Consultant, Environmental Sciences*

EXPOSURE OF FOREST WORKERS TO 2,4,5-T:
' CALCULATED DOSE LEVELS

J. C. Ramseyl, T. L. Lavy2 and W. H. Braun*

).-

MAR 1979

MAR 1979

1
2

Toxicology Laboratory, Dow Chemical Company USA, Midland, Michigan.

Altheimer Laboratory, University of Arkansas.

�EXPOSURE OF FOREST WORKERS TO 2,4,5-T:
CALCULATED DOSE LEVELS'

SUMMARY

This report presents calculated dose levels of 2,4,5-T in
workers following application of 2,4,5-T in forestry operations. Experiments were conducted with 19 male and 2 female
workers engaged in the application of the propylene glycol
butyl ether (PGBE) ester of 2,4,5-T (ESTERON® 245 herbicide)
by helicopter (both raindrop nozzle and microfoil boom), by
backpack spraying, and by tractor-mounted mist blowers.1

No

special instructions or safety precautions were used. Urine
samples were collected following each application and
analyzed for 2,4,5-T. The amount of 2,4,5-T absorbed by
each worker was calculated by pharmacokinetic analyses of
the urinary excretion data using three different methods.
The results were classified by the worker's job description
and the average dose levels of 2,4,5-T were as follows,
calculated as mg 2,4,5-T per kg of body weight.

Mixers,

0.073+0.046; backpack sprayers, 0.063+0.034; tractor drivers,
0.045+0.007; supervisors, O.OlliO.Oll; helicopter flagmen,
0.002±0.003.

The two helicopter pilots had average calculated

dose levels of 0.007 and 0.048 mg/kg. These dose levels of
1

T. L. Lavy, Altheimer Laboratory, University of Arkansas.

©Trademark of The Dow Chemical Company.

�-2-

2,4,5-T are far below the 20 mg/kg no effect level for
teratogenic or fetotoxic effects.

Therefore, we conclude

that under these conditions the absorption of 2,4,5-T
presents a negligible toxic hazard to forest workers.

INTRODUCTION

Basic toxicological principles require a knowledge both of
the inherent toxicity of a chemical and of the quantity
actually absorbed into the body in order to assess its
possible hazard.

The quantity of chemical absorbed may be

quite different from the quantity to which workers are
exposed under field conditions.

Therefore, a proper assess-

ment of the potential hazard to workers during pesticide
applications in the field is dependent on reliable estimates
of the quantity of pesticide absorbed under these conditions.
The amount of 2,4,5-T absorbed by applicators of 2,4,5-T
formulations in forestry operations has never been directly
measured.

A study was recently conducted by T. L. Lavy (1)

which provides urinary excretion data from which estimates
can be made of the amount of 2,4,5-T absorbed by forestry
workers during the application of 2,4,5-T. Four experiments
were conducted with 19 male and 2 female workers engaged in
the application of the propylene glycol butyl ether (PGBE)
ester of 2,4,5-T (ESTERON® 245 herbicide) by helicopter

�-* *3 _^

(both raindrop nozzle and microfoil boom), by backpack
spraying, and by tractor-mounted mist blowers. Total voided
urine samples were collected for each worker both prior to
and following application, and measurements were made of the
amount of 2,4,5-T excreted.

The forest applications were

made by personnel normally engaged in this type of work and
all operations were carried out in the usual manner.

No

special instructions or safety precautions were used. The
field conditions of the studies as well as the results of
the analyses are reported in detail by Lavy (1).

The total amount of 2,4,5-T excreted in the urine following
exposure represents a minimum estimate of the amount of
2,4,5-T absorbed, since urinary excretion may not be complete
at termination of the experiment.

However, calculation of

the absorbed dose of 2,4,5-T based on pharmacokinetic analysis
of urinary excretion data is not dependent on total excretion
and can therefore provide a more realistic estimate of the
absorbed dose. Furthermore, this approach provides a sound
statistical basis for evaluating the adequacy of the pharmacokinetic model to explain the observed data.

It is the

purpose of this paper to report estimates of the amount of
2,4,5-T absorbed by these workers, based on pharmacokinetic
analyses of the amount of 2,4,5-T excreted in the urine.

�-4-

METHODS

Pharmacokinetic Model
In order to establish an adequate pharmacokinetic model
for the absorption and excretion of 2,4,5-T, the following
data were considered.

Previous studies with 2,4,5-T ingested by human volunteers
at a dose level of 5 mg per kg body weight showed that
essentially all of the 2,4,5-T was quickly absorbed and
excreted unchanged in the urine (2). Urinary excretion of
2,4,5-T occurred by an apparent first order process with a
half life of 23.1 hr (0.96 day). The fecal route of excretion was shown to be negligible for 2,4,5-T in humans.

In rats given a single oral dose of 5 mg/kg, the 2,4,5-T
was excreted mainly in the urine by an apparent first order
process with a half-life of 13.6 hr (3).

In another study,

in rats given a single intravenous dose of 5 mg/kg (4),
urinary excretion of unchanged 2,4,5-T accounted for 96% of
the administered dose and excretion occurred by an apparent
first-order process with a half-life of 10.7 hr. Thus, the
urinary excretion of 2,4,5-T at this dose level occurs by a
first order process that is essentially independent of the
route of administration.

�-5-

A recent study conducted in this laboratory (5) showed that
the PGBE ester of 2,4,5~T applied to the shaved skin of rats
at a dose level of 5 mg/kg was virtually completely absorbed,
and subsequently excreted in the urine as 2,4,5-T per se.
Urinary excretion of 2,4,5-T appeared to be a first order
process with a half-life of approximately 24 hr, indicating
that the dermal absorption process may have been slow in
relation to the urinary excretion of 2,4,5-T.

The foregoing data demonstrate that measurement of the
urinary excretion of 2,4,5-T can provide a reliable estimate
of the amount of 2,4,5-T absorbed. Also, it is apparent
that esters of 2,4,5-T are slowly but readily absorbed
through the skin and are then excreted in the urine as
2,4,5-T acid.

These considerations provide the basis for

the pharmacokinetic model shown in Figure 1 for the absorption of 2,4,5-T or its esters and subsequent urinary
excretion of 2,4,5-T in humans. A definition of symbols and
terms is given in the legend of Figure 1. All calculations
have been made on the basis of 2,4,5-T acid equivalents.

�SCt)-

0,

Bft)

Figure 1. Schematic diagram of the pharmacokinetic
model for the absorption of 2,4,5-T or its PGBE
ester in humans, followed by urinary excretion of
2,4,5-T acid. S(t) - amount of 2,4,5-T remaining to be
absorbed at time t. B(t) • amount of 2,4,5-T in body
at time t. E(t) - amount of 2,4,5-T excreted in urine
at time t. k and kje « first order rate constants for
absorption and excretion of 2,4,5-T, respectively.

The differential equations and initial conditions describing
the dynamics of the pharmacokinetic model are shown in Figure
2. The half -life for the urinary excretion of 2,4,5-T in
humans previously determined as 0.96 day (2) corresponds to
an apparent first order elimination rate constant of 0.72
day" , the value we have used for k. 6 in the differential
*
equations of Figure 2.

The value of S(t) at time zero

represents the dose D , which is the total quantity of
2,4,5-T absorbed.
Differential Equation

Initial Condition

dt
dt

dt
Figure 2. Differential equations and initial conditions describing
the pharmacokinetic model of Figure 1.

�-7-

Data Base
The urinary excretion data reported by Lavy in Tables 6, 7,
8, and 9 of reference 1 were treated as follows.

Since a

large amount of diurnal variation was evident in the urine
samples collected at 12-hr intervals, the values for successive 12-hr intervals were combined so that each value
represents the amount of 2,4,5-T excreted per day.

Urine

samples collected on the day previous to either the first or
the second application date were considered to be preexposure samples.

The data thus arranged are shown in Table

1, with the same designation used by Lavy for each worker (1).

The amount of 2,4,5-T in the pre-exposure samples fluctuated
widely with no apparent pattern, therefore no background
corrections were applied.

The workers employed as mixers

may have been exposed on the day previous to the application
date (since the formulations are usually mixed the day
before the actual application), but for purposes of pharmacokinetic analysis they were considered to be exposed only on
the date of application.[ The duration of the application
1
procedures ranged from 55 minutes to approximately 4 hours
(average 138 minutes).

Since this is a short time span

relative to the total duration of the experiments (up to
seven days), the calculated dose was considered to be a
single application to the skin at time zero.

These assumptions

have either a negligible or a maximizing influence on the
calculated dose absorbed.

�' -f*
-8-

TABLE 1. Daily and Total Amounts of 2,4,5-T Excreted in the Urine of Forest
Workers Following Application of ESTERON® 245a
Worker
No. b
1A
IB
2A
2B
3A
3B
4A
4B
5A
5B
6A
7A
7B
8A
8B
9A
9B
10A
10B
11A
11B
12A
12B
13A
13B
14A
14B
ISA
15B
16A
16B
17A
17B
18A
18B
19A
19B
20A
20B
21A
21B

mg 2,4,5-T Excreted

Day 0
0.119
0,039
0.398
0.784
nd

0.246
0.146
0.749
0.033
0.098
0.373
0.796
0.314
0.088

c

Day l "
0.182
0.169
0.611
2,067
0.472
1.142
0.254
0.402
0.133
0.193
0.572
0.211
0.931
0.698

-

-

0.103
0.097
0.690
0.953
0.037

0.343
0.644
0.709
0.889
1.246

nd
nd

nd

Day 2
0.210
0.122
1.458
0.911
1.100
0.237
0.913
1.101
0.772
0.367
1.027
3.701
0.708
0.858
0.277
1.500
0.716
0.748
1.068
2.272
1.632

Day 3
0.127
0.167
1.460
0.978
1.648
0.515
0.421
0.584
0.251
0.126
0.458
0.856
0.368
0.579
0.196
0.687
0.548
0.773
0.539
1.653
1.204
0.041
0.267
1.827
1.344
0.109
0.038

nd

nd

nd

0.012
0.020

0.099
0.008

0.310
1.409
1.397
0.029
0.060
0.035

nd

nd

nd

1.894
1.362

0.026
nd

0.288
0.324
0.715
0.960
nd

0.047
nd
nd
nd
nd

0.230
2.430
1.470

0.008
0.020
0.467
0.370
1.610
1.112
0.014
0.018
0.070
nd
nd
nd

0.053
0.037
0.602
0.812
1.229
3.536
0.158
0.057
0.079
0.022
0.029
0.016

nd

'

nd
0.107
0.014
0.383
0.600
0.883
2.229
0.113
0.032
0.064

Day 4
0.155
0.203
0.723
0.646
0.618
0.549
0.495
0.506
0.222
0.122
0.235
0.876
0.422
0.380
0.146
0.599
0.478
0.761
0.892
0.629
0.283

Day 5
0.085
0.198
0.422
0.464
0.218
0.214
0.279
0.597
0.101
0.074
0.214
0.760
0.334
0.259
0.134
0.372
0.278
0.498
0.893
0.408
0.279

nd

nd

0.097
1.386
0.964
0.155
0.010

0.084
1.136
0.737
0.032
0.081
0.097

nd
nd
nd
nd

nd
nd
nd

Day 6
0.075
-

1.212
-

0.267
-

0.494
-

0.142
-

0.566
_

-

0.069
-

0.773
-

0.031
nd
nd

0.255

0.409
0.602
0.916
2.428
0.073

0.365
0.455
0.804
1.650
0.067

nd

nd
nd
nd
nd

0.022

0.089

-

0.016

nd

nd

0.033
0.022

0.032
0.011

-

0.465

0.116
nd
-

Totald
0.834
0.859
5.886
5.066
4.323
2.657
2.856
3.190
1.621
0.882
2.506
6.970
2.763
2.775
0.753
3.501
2.664
3.489
4.281
6.208
3.398
0.041
1.057
8.188
6.685
0.325
0.319
0.140
nd

0.168
0.071
2.481
2.839
5.907
10.955
0.541
0.107
0.229
0.022
0.116
0.138

Data taken from Lavy ( )
1.
A and B refer to the first and second exposure, respectively.
cThe beginning of day 1 is designated as the beginning of the exposure.
Excluding the 2,4,5-T excreted on day 0 (the "pre-exposure" sample).
e
- means no data available; nd means 2,4,5-T below detection limit in urine.

�-9-

In order to estimate the actual amount of 2,4,5-T absorbed
(calculated as mg 2,4,5-T) during each application, the
following three methods were used.

Method A
This method is based on pharmacokinetic parameter estimation
techniques in which the best parameter estimates are considered to be those that yield the closest fit of the
calculated data to the observed data (using the least squares
criterion).

In this case, parameter estimates were desired

for the absorption rate constant (k
absorbed dose of 2,4,5-T (DQ).

) and for the total

The excretion rate constant

(kle) was set at the previously established value of 0.72
observed data consisted of mg 2,4,5-T excreted
day~ , and the observ&lt;
in the urine per day.

The data for each worker following both exposures were
plotted on semi-logarithmic graph paper.

Visual inspection

of all these plots showed that there were 12 exposures for
10 different workers in which (a) the data were complete (no
missing data points), and (b) the time course of urinary
excretion of 2,4,5-T followed a kinetically consistent
pattern (i.e., a rise following the application date and a
subsequent log-linear decline).

These data sets were

consistent with the model shown in Figure 1.

�I,*
V-'

-10-

Pharmacokinetic parameter estimation for these 12 data
sets was accomplished with a digital computer, and the
average percent variation explained was 69.0% (range
29.5% to 93.5%). The results of these analyses are shown in
Figures 3 (a) through 3(&amp;) in which the points • and o
represent the observed and calculated data points, respectively,
As expected, the estimated values of D varied considerably
between individuals. However, the apparent first-order
absorption rate constant k

was reasonably consistent

between individuals, the average value being 0.92 day~ with
a standard deviation of 0.21 day"

(n = 12) . The foregoing

analyses thus provided an estimate of the absorbed dose of
2,4,5-T for 12 of the 41 exposures comprising the complete
study. The results are shown in column A of Table 2. Also,
the average value of the absorption rate constant determined
here was used in the following two methods to obtain further
estimates of the absorbed dose.
Method B
Integration of the differential equations of Figure 2 and
solution for the total amount of 2,4,5-T excreted in the
urine t days following exposure, designated as E(t), results
in equation 1.

CD

�• Observe
O Calculi

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: . . { . ; • ; •

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D (CalcJ = 0.90 mg
o
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DQ (Calc) = 4.26 mg
Calc)
4.

Worker No. 4 (A)
D (Calc) = 2.76 mg

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Worker No. 9 A
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( a c
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. 4

Figure 31

1

3

Day
Worker No. 9 B
( )
DQ

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. 9

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3
Day

Day

Worker No. 11(A)
D (Calc) = 6.4? mg
ale)
6.45

1

Worker No. 12 (B)
D (Gale) = 1.06 mg
le)
1.06
Figure 31

i

�-17-

TABLE: 2. Calculated Amount of 2,4,5-T Absorbed by Forest Workers During
Application of ESTERON® 245

wortter
No. a
1A
IB

2A
2B
3A
3B
4A
4B
5A
5B
6A
7A
7B
8A
8B
9A
9B
10A
10B
11A
11B
12A
12B
13A
13B
14A
14B
15A
15B
16A
16B
17A
17B
ISA
18B
19A
19B
20A
20B
21A
21B

Method A
0.898
-

5.153
-

4.262
-

2.755
-

1.561
0.947
2.644
-

3.086

Method B
0.875
0.943
6.175
5.564
4.535
2.918
2.996
3.504
1.701
0.969
2.752
7.312
3.035
3.048

-

-

3.844
3.085

3.845
2.926
3.832
4.702
6.818

-

6.450
-

1.063
nd
-

-

0.059
1.109
8.993
7.013
0.357
0.335
0.154
nd

0.241
0.102
2.603
3.118
6.197
12.032
0.568
0.153
0.275
0.112
0.113
0.152

Method Cb
"y""~i.040 ± 0.408 (6)
1*221 ± 0.833 (5)
1
9.016 ± 9.539 (6)
5.804 ± 2 . 8 4 0 (5)
4.585 ± 2.030 (6)
3.173 ± 1.884 (5)
4.206 ± 3.720 (6)
4.003 ± 2.175 (5)
1.800 ± 1.005 (6)
0.941 ± 0.248 (5)
2.624 ± 0.719 (5)
6.842 ± 4.667 (6)
3.270 ± 1.260 (5)
3.077 ± 0.365 (5)
1.169 ± 0.373 (4)
3.877 ± 1.410 (5)
3.088 ± 0.527 (5)
4.369 ± 1.574 (5)
.766 ± 3.513 (5)
.373 ± 1.449 C5)
.240 ± 1.732 (4)
0.190
'(1)
1.151 ± 0.290 (6)
1(T.130 ± 3.704 (5)
L_ 8.882 ± 4.750 (6)
0.541 ± 0.439 (4)
0.455 ± 0.374 (6)
0.469 ± 0.673 (3)

d

nd

0.241
0.099
3.323
3.560
7.431
13.501
0.877
0.147
0.262
0.077
0.251
0.345

±
±
±
±
±
±
±
±
±

0.233
0.032
1.653
1.572
2.905
6.143
0.934
0.054
0.102

(3)
(3)
(6)
(5)
(6)
(5)
(6)
(3)
(4)
(1)
± 0.184 (4)
± 0.532 (4)

A and B refer to the first and second exposure, respectively.
The number of individual determinations of D by Method C is shown in parentheses.

3

�-18-

Solution of equation (1) using the previously determined
values of k01 and k ie at successive values of t reveals the
cumulative fraction of the absorbed dose of 2,4,5-T that is
excreted in the urine following exposure.

The values of

this fraction obtained from 1 through 7 days following
exposure are given in Table 3.
TABLE 3. Cumulative Fraction of the Absorbed Dose of
2,4,5-T Excreted in the Urine

Days Following
Exposure

Cumulative Fraction of
Dose ExcretedV:

1

0.1956

2
3
4
5
6
7

0.4819
0.6974
0.8326
0.9105
0.9532
0.9760

The absorbed dose D was calculated by dividing the cumulative
quantity of 2,4,5-T excreted in the urine by the appropriate
fraction at that time.

This procedure provided a single

estimate of the absorbed dose for 39 of the 41 exposures,
shown in column B of Table 2.

Method C
By using the integrated form of the equation for the cumulative
quantity of a chemical excreted as a function of time, an
equation can be derived with which the absorbed dose can be

�•f
V- •*• -v

-19-

calculated based on the interval (in this case, daily1
amount

of 2,4,5-T excreted using the previously esta-

blished values for Ic

and k ie (7) . This calculation is

based on equation 2 where E. is the amount of 2,4,5-T
excreted during the i-th day following exposure, d. is the
length of the collection interval (1 day), and t. is the
total number of days following exposure.
D

The calculation of

by this method is independent of the total (cumulative)

quantity of urine collected.

C2)

Application of equation 2 therefore provided an estimate of
the absorbed dose every day on which urine was collected
following each of the 41 exposures comprising the study.
The results shown in column C of Table 2 are the average
calculated dose (± standard deviation) for each exposure by
this method.

�-20-

RESULTS

Table 2 shows the calculated dose of 2,4,5-T following each
exposure to the 21 workers in this study.

A comparison of

the data in Table 2 reveals similar results by all three
methods used to calculate the dose.

As expected, these

calculated doses are almost always greater than the total mg
of 2,4,5-T excreted in the urine at the end of 5 or 6 days
following exposure (last column in Table 1).

The maximum (i.e., worst case) estimated dose shown in Table
2 for each exposure was used to calculate the dose in mg
2,4,5-T per kg body weight for each worker. These dose
levels are shown in Table 4, 5, 6 and 7 for the four types
of spray application included in this study.

It is apparent

from inspection of these tables that the quantity of 2,4,5-T
absorbed by the workers was usually less than 0.1 mg/kg. In
fact, only two doses exceeded this level; a backpack sprayer
(No. 2, second exposure) with a calculated dose of 0.132
mg/kg, and a mixer (No. 18, second exposure) with a calculated
dose of 0.156 mg/kg. The lowest dose level of 0.001 mg/kg
was received by flagmen for helicopter applications.

Since there was an obvious correlation between the job
descriptions of the workers and the calculated dose levels
of 2,4,5-T, the results were grouped on the basis of job
descriptions. The average dose levels thus obtained are

�-21-

TABLE 4.

WORKER

CALCULATED DOSE OF 2,4,5-T TO FOREST WORKERS:
BACKPACK SPRAYER APPLICATION

BODY
WEIGHT

MAXIMUM
CALCULATED
DOSE OF 2,4,5-T

(Kg)

JOB
DESCRIPTION

EXPOSURE

1 (M)

72.6

Mixer/Supervisor

First
Second

0.014
0.017

2 (M)

68.1

Sprayer

First
Second

0.132
0.085

3 (F)

49.9

Sprayer

First
Second

0.092
0.064

4 (M)

95.3

Sprayer

First
Second

0.044
0.042

5 (F)

52.2

Sprayer

First
Second

0.034
0.019

6 (M)

65.8

Sprayer

First

0.042

7 (M)

74.9

Sprayer

First
Second

0.098
0.044

(a ex )

�-22-

TABLE 5.

CALCULATED DOSE OF 2,4,5-T TO FOREST
WORKERS:
TRACTOR MOUNTED MIST BLOWER APPLICATION

WORKER
(sex)

BODY
WEIGHT
_ (kg)

JOB
DESCRIPTION

EXPOSURE

MAXIMUM
CALCULATED
DOSE OF 2,4,5-T
Cmg/kg)

8 (M)

95.3

Supervisor

First
Second

0.032
0.012

9 (M)

84.0

Driver

First

0.046
0.037

Second
10 (M)

106.7

Driver

First

Second
11 (M)

79 . 5

Mixer

0.041
0.054

First
Second

0.086
0.053

�-23-

TABLE 6.

CALCULATED DOSE OF 2,4,5-T TO FOREST WORKERS:
HELICOPTER (MICROFOIL BOOM) APPLICATION

MAXIMUM
CALCULATED
DOSE OF 2,4,5-'
(mg/kg)

WORKER
(sex)

BODY
WEIGHT
(kg)

12 (M)

95.3

Pilot

First
Second

0.002
0.012

13 (M)

109. Q

Mixer

First
Second

0.092
0.081

14 (M)

84.0

Supervisor

First
Second

0.006
0.005

15 (M)

61.3

Flagman

First
Second

0.008
nd*

16 (M)

74.9

Flagman

First
Second

0.003
0.001

*Not detected.

JOB
DESCRIPTION

EXPOSURE

�-24-

TABLE 7.

(e.
sx)

CALCULATED DOSE OF 2,4,5-T TO FOREST
WORKERS:

HELICOPTER (RAINDROP NOZZLE) APPLICATION
MAXIMUM
BODY
CALCULATED
DOSE OF 2,4,5-'
JOB
WEIGHT
EXPOSURE
DESCRIPTION
(ma/ka)
(ka&gt;

17 (M)

72.6

Pilot

First
Second

0.046
0.049

18 (M)

86.3

Mixer

First
Second

0.086
0.156

19 (M)

81.7

Supervisor

First
Second

0.011
0.002

20 (M)

86.3

Flagman

First
Second

0.003
0.001

21 (M)

95.3

Flagman

First
Second

0.001
0.002

�-25-

TABLE 8.

AVERAGE CALCULATED DOSES OF 2,4,5-T
TO FOREST WORKERS

JOB
DESCRIPTION

TOTAL NUMBER
OF EXPOSURES

Mixers

AVERAGE CALCULATED
DOSE OF 2,4,5-T(mg/kg)
Dev.

8

0.07310.046

11

0.06310.034

Tractor Drivers

4

0.04510.007

Supervisors

6

0.01110.011

Helicopter Flagmen

8

0.00210.003

Backpack Sprayers

Helicopter Pilot (No. 12)

2

0.007

Helicopter Pilot (No. 17)

2

0.048

�-26-

shown in Table 8.

The mixers, backpack sprayers, and

tractor drivers had average dose levels of 0.073±0.046,
0.063±0.034, and 0.045±0.007 mg/kg respectively.

The

average dose level calculated for all the workers in these
groups (n=23 exposures) was 0.063+0.036 mg/kg.

The super-

visors and helicopter flagmen showed average dose levels of
O.OlliO.Oll and 0.002+0.003 mg/kg respectively.

The two

helicopter pilots had average dose levels during the two
applications of 0.007 and 0.048 mg/kg.

DISCUSSION

The general validity of the linear pharmacokinetic model
used to obtain the dose estimates reported here is attested
by the reasonable fit of the observed and theoretical data
points shown in Figures 3(a) through 3(£).
three methods of calculating D

While any of the

should provide a valid

estimate, Method C (the use of the interval amounts of
2,4,5-T excreted) is believed to yield the best overall
value, since each daily urinary output of 2,4,5-T carries
equal weight in calculation of the average dose absorbed for
a given exposure.

The generally excellent agreement between

the three methods of calculating D
support to the above conclusions.

(Table 2) lends further

�-27-

The pattern of the daily amount of 2,4,5-T excreted in the
urine following exposure is characterized by a maximum on
day 2, followed by a steady log-linear decline thereafter
(see the calculated data points in Figure 3) . However, an
examination of the data in Table 1 shows that, in many
j
cases, there is a significant increase in the amount of
2,4,5-T excreted after the second day following exposure.
These data are inconsistent with the excretion pattern
expected from a single exposure (2) , and may indicate
subsequent exposure to 2,4,5-T or to its ester after the
actual application date.

The speculation that such ex-

posures might arise from the use of contaminated clothing or
footgear should be verified by further experiments and
observations.

In each case, these increased amounts of

urinary 2,4,5-T have the effect of increasing the calculated
dose, and therefore result in maximized estimates of the
dose absorbed on the application date.

Since the data reported by Lavy (1) indicate clearly that
the respiratory route of exposure to 2,4,5-T is virtually
negligible, we have assumed that most of the absorbed dose of
2,4,5-T is the result of dermal exposure to ESTERON 245
herbicide formulations.

However, the methods used here to

calculate the absorbed dose are, in effect, independent of
the actual route of administration and will reflect the
total amount of 2,4,5-T absorbed by all possible routes.

�-28-

The pharmacokinetic model describing the absorption and
excretion of 2,4,5-T in humans can also be used to predict
the accumulated body burden of 2,4,5-T that would result
from repeated daily exposures (6).

The results of this

mathematical simulation are shown by the solid line in
Figure 4.

These simulated data predict that the maximum

accumulated body burden of 2,4,5-T resulting from repeated
daily exposures would be 1.4x the daily dose D . In other
words, if a worker absorbed a dose of 0.05 mg/kg each day,
the maximum body burden attained would be 0.07 mg/kg and
this maximum would be reached after approximately 7 daily
exposures.

However, if the 2,4,5-T remaining to be absorbed

were removed 6 hr after each exposure (e.g., by washing or
changing clothing), the predicted accumulated body burden
would be represented by the dotted line in figure 4.

In

this case, the maximum body burden would be 0.3x the daily
dose D , and this maximum would be reached after approximately 3 daily exposures.

In summary, the amount of 2,4,5-T absorbed by forest workers
during the application of ESTERON® 245 has been shown to be
generally less than 0.1 mg 2,4,5-T per kg of body weight.
Since this dose level is far below the no effect level of 20

�-29-

mg/kg for fetotoxic or teratogenic effects cited by EPA (8),
we conclude that under these conditions the absorption of
2,4,5-T presents a negligible toxic hazard to forest workers,

WRITTEN BY:

//i a./??

JoHn C . Rams ey , Ph . D
Bio trans format ion Group

Terry L. Lavy^ Ph.D.
Altheimer Laboratory
University of Arkansas

Werner H. Braun
Group Leader, Biotransformation

REVIEWED BY:

Group

�2.8
2.6 2.4 2.2 2.0 -

D

1.8
1.6
1.4
1.2
1.0
0.8
0.6
0.4

I

oo
o
I

0.2
0
0

3

4

8

9

10

11

12

13

14

15

16

17

18

19 20

Days
Simulated body burden of 2,475-T following 13 repeated daily exposures in units of the
daily dose D .
Solid Line=body burden if, 2,4,5rT continuously absorbed.
Dotted Line=body burden if 2,4,5-T remaining to be absorbed is removed 6 hours after
each exposure.
Figure 4

�-31REFERENCES

(1) T. L. Lavy. Measurement of 2,4,5-T Exposure of Forest
Workers.

Project Completion Report to National Forest

Products Association.

November, 1978.

(2) P. J. Gehring, C. G. Kramer, B. A. Schwetz, J. Q. Rose,
and V. K. Rowe.

The Fate of 2,4,5-Trichlorophenoxyacetic

Acid (2,4,5-T) Following Oral Administration to Man
Tox. Appl. Pharmacol.

26, 352-361 (1973).

(3) W. N. Piper, J. A. Rose, M. L. Leng, and P. J. Gehring.
The Fate of 2,4,5-Trichlorophenoxyacetic Acid (2,4,5-T)
Following Oral Administration to Rats and Dogs. Tox. Appl.
Pharmacol. 26_, 339-351 (1973) .

(4) M. W. Sauerholf, W. H. Braun, G. E. Blau, and P. J.
Gehring.

The Dose-Dependent Pharmacokinetic Profile of

2,4,5-Trichlorophenoxyacetic Adid Following Intravenous
Administration in Rats.

Tox. Appl. Pharmacol 3_6_, 491-

501 (1976).

(5) J. D. Young, J. C. Ramsey, and W. H. Braun.

Pharmaco-

kinetics of 2,4,5-T PGBE Ester Applied Dermally to Rats.
The Dow Chemical Company, Midland, Mich. Manuscript in
Preparation -

�-32-

(6) Continuous System Modeling Program III.
Reference Manual.

IBM No. SH 19-7001-2.

Program
1972.

(7) J. C. Ramsey, G. E. Blau, and P. J. Gehring.
Pharmacokinetic Modeling Based on Interval Excretion
Data.

The Dow Chemical Company, Midland, Mich.

Manuscript in Preparation.

(8) EPA. Rebuttable Presumption Against Registration and
Continued Registration of Products Containing 2,4,5-T,
Federal Register 43 (78), 17116-17157, April 21, 1978.

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              <name>Title</name>
              <description>A name given to the resource</description>
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                  <text>Alvin L. Young Collection on Agent Orange</text>
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              <name>Description</name>
              <description>An account of the resource</description>
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                  <text>&lt;p style="margin-top: -1em; line-height: 1.2em;"&gt;The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young.&lt;/p&gt;&#13;
&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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      <name>Text</name>
      <description>A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text.</description>
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        <element elementId="52">
          <name>Box</name>
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              <text>043</text>
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          <name>Folder</name>
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              <text>1038</text>
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              <text>Series III Subseries I</text>
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          <element elementId="39">
            <name>Creator</name>
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                <text>Sauerhoff, M. W.</text>
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                <text>M. B. Chenoweth</text>
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              <elementText elementTextId="13470">
                <text>R. J. Karbowski</text>
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              <elementText elementTextId="13471">
                <text>W. H. Braun</text>
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                <text>J. C. Ramsey</text>
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                <text>P. J. Gehring</text>
              </elementText>
              <elementText elementTextId="13474">
                <text>G. E. Blau</text>
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            <name>Source</name>
            <description>A related resource from which the described resource is derived</description>
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              <elementText elementTextId="13477">
                <text>Journal of Toxicology and Environmental Health</text>
              </elementText>
            </elementTextContainer>
          </element>
          <element elementId="40">
            <name>Date</name>
            <description>A point or period of time associated with an event in the lifecycle of the resource</description>
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              <elementText elementTextId="13478">
                <text>1977</text>
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          <element elementId="50">
            <name>Title</name>
            <description>A name given to the resource</description>
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                <text>Fate of Silvex Following Oral Administration to Humans</text>
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          </element>
          <element elementId="49">
            <name>Subject</name>
            <description>The topic of the resource</description>
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              <elementText elementTextId="13481">
                <text>human testing</text>
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        <name>ao_seriesIII</name>
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