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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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01027

Author
Corporate Author

USDA-States-EPA 2,4,5-T RPAR Assessment Team

Report/Article Title The Biologic and Economic Assessment of 2,4,5-T

Journal/Book Title
Year

1979

Month/Day

February 15

Color

U

Number of Images

15

DOSCrlptOU Notes

Alvin L- Youn9filed tnis item under the category
"Human Exposure to Phenoxy Herbicides and TCDD"

Friday, March 30, 2001

Page 1027 of 1070

�FINAL DftAFT REPORT
*

ALVIN L YOUNG, Major, USA*
Consultant, Environmental Sciences

THE BIOLOGIC AND ECONOMIC
ASSESSMENT OF 2,4,5 - T

-

A REPORT OF THE
USDA-STATES-EPA

2,4,5-TRPAR ASSESSMENT TEAM

February 15, !979

�ESTIMATION OF EXPOSURE BY THE ABSOLUTE METHOD

The absolute method of estimating exposure uses a combination of
assumptions and direct measurements. The assumptions are geared to
particular applicator exposure situations as described in the section on
"Exposure of Applicators According to Use Pattern" in Part 5 of Chapter
5.
These assumptions and direct measurements have been applied to exposure
situations as they exist in the field. Clothing described are the kinds
actually used. Estimates of skin area exposed are believed to be
accurate for the types of clothing described.
The direct measurements involve data from two experiments: (1) a
2,4,5-T dermal absorption experiment involving four human volunteers In
a laboratory experiment (Newton 1978) and (2) a field experiment in
which 2,4,5-T deposition (and absorption) was measured during
operational application by helicopter (5 Individuals), tractor sprayer
(5 individuals), and backpack sprayer (12 individuals) (Lavy 1978a&amp;b).
In the first part of this section the various assumptions are used with
the data from the laboratory experiment to calculate maximum absorption
(exposure) levels for particular exposure situations. The absorption
(exposure) levels from the field experiment are used to calculate
exposure as It occurs during actual use. In the second part of this
section, exposure levels from both sources are presented in narrative
form for each method of 2,4,5-T application in each of the four
commodity groups.
EXPOSURE CALCULATED FROM A LABORATORY EXPERIMENT

Assumption Sets
The likelihood of an applicator or observer in spray operations being
exposed to a given level of 2,4,5-T depends on the physical
5-177

�circumstances during exposure. A series of sets of assumptions have
been developed which describe the nature and extent of the exposure of
applicators involved with particular types of application. Each set of
assumptions closely approximates the actual conditions in which the
chemical Is used, based on experience of Assessment Team members and
users in Oregon, Texas, Arkansas, California, Indiana, and Pennsylvania
(Norris et al. 1979). Table 30 identifies the type of application (or
situation) associated with each assumption set, and some of its
conditions.
There are five sets of assumptions for ground spray workers and five for
aerial spray workers. The various situations are those typical for
backpack sprayer operators, tractor sprayer operators, tree Injection
personnel, aircraft mixer-loaders, and flaggers. Conditions for pilots
were not described because they are protected more than the other
workers. Each set embodies different assumptions relating to the
concentration of spray mixture, protective clothing, skin exposed, and
skin absorption. In addition there are 2 sets of assumptions from
PD-1. In general, the assumptions in sets 1 through 10 are different
from those used in PD-1 (EPA 1978). An explanation for the choices used
follows.
Concentration of Spray Material
Concentrations of 2,4,5-T greater than 16 Ib acid equivalent per hundred
gallons (aehg) are seldom used in ground equipment. The higher cost for
higher concentrations which do not substantially increase effectiveness
precludes widespread use. None of the widely used products recommends
higher than 6 aehg in water for general use; 2 to 4 aehg is more widely
used. The rates of 8 to 16 aehg used here are in the upper range for
oil sprays, but they are used with sufficient frequency to warrant
calculations as upper limits of ordinary exposure. Higher
concentrations are limited to mist blowers and aircraft.

5-178

�Table 30—Typical Job descriptions of workers exposed under assumption sets
listed in Tables 31 and 32
Assumption ect
1
2

3

4
5
PD-1 a
6
7
8

9

10

PD--1 b

Job description
Tractor mounted boom sprayer on rice levees
or range and pasture lands
Backpack or handgun operator in right-of-way or
rangeland basal spray operation, with gloves
and long-sleeve shirt
Backpack, handgun or mistblower operator
in forest or power line basal spray operation,
short-sleeve shirt, no gloves
Same as 3, with long-sleeve shirt and gloves
Hypo-hatchet tree injector operator, 2,4,5-T
amlne, long-sleeved shirt, gloves
Backpack spray operator without protection as
described in PD-1
Helicopter mechanic-mixer, light (common) dose,
gloves and long-sleeved shirt
Helicopter mechanic-mixer maximum concentration,
wearing gloves and long-sleeved shirt
Flag person, 1 Ib/A 2,4,5-T in 3 gpa, wearing
broad-brim hat, long-sleeved shirt
Exposure is derived as follows: flogger fails
to move out of spray swath once for each 10
passes of the spray plane, or 4 times per hour.
This gives an exposure of 1.042 mg 2,4,5-1.
Flag person, 2 Ib/A 2,4,5-T in 5 gpa, wearing
broad-brim hat, long-sleeved shirt.
Exposure Is as the same basis as in assumption
8, but adjusted by a factor of 2 for the higher
rate of application. This gives an exposure of
2.084 mg 2,4,5-T.
Flag person, 2 Ib/A 2,4,5-T in 5 gpa without
protective clothing
Exposure is as the same basis as in assumption
8, but adjusted by a factor of 2 for the higher
rate of application and a factor of 8 for the
greater degree of absorbtion due to less
clothing.
Flag person described in PD-1, with both dermal
and inhalation exposure

5-179

�Protective Clothing
Protective clothing of some kind is normally worn by all pesticide
applicators. Long-sleeved shirts alone reduce exposure substantially
below that of a tee shirt. Use of gloves and a long-sleeved shirt
reduces skin exposure to 12.3 percent of that received when the
applicator wears a short-sleeved shirt and no gloves (Wolfe et al.
1974). Addition of a wide-brim hat to long-sleeved shirt and gloves
reduces exposure to 8.8 percent. Assumption sets 2, 4, and 5 for,
ground application and 6 and 7 for aerial application provide for
long-sleeved shirts and gloves as protective clothing. This reduces
exposure to 12.3 percent of the two square feet of skin surface
estimated to be exposed to spray mixtures when a short-sleeved shirt and
no gloves are used (assumption sets 1, 3 and PD-la). Assumption sets 8
and 9 for flaggers involved with aerial applications include broad-brim
hard hats, long-sleeved shirts, and gloves.
Dermal Absorption
In a previous section (The Factorial Method) the inappropriate use of
the 10 percent 2,4,5™T absorption figure in PD-1 was discussed and a
factorial correction factor developed. Unfortunately there are very
limited data on which human exposure (via dermal absorption) to 2,4,5-T
can be estimated. In this section we use data from a preliminary
experiment involving humans as a basis for calculating 2,4,5~T
absorption from dermal exposure (Newton 1978). In this experiment, four
human volunteers were exposed to one of four spray solutions containing
2,4,5-T at concentrations of 2, 4, 16, or 32 aehg. The exposure
involved placing a 144 square inch denim cloth soked with 40 ml of the
appropriate spray mixture on the sking of one upper thigh. The cloth
was covered and bound tightly in place with plastic wrap to insure good
contact with the skin and to prevent drying. The skin was wet to
saturation throughout the 2-hour exposure period. The assumption is
this type of exposure results in maximum dermal uptake because the skin
is as wet as it can be without the spray running off and the soaked

5-180

�cloth provides a reservoir of chemical to replace any that is removed by
dermal absorption.

At the end of the 2 hour exposure period, the cloth

was removed and the treated area washed with alcohol and wiped dry.
Urine was then collected for 5-24 hour periods.

2,4,5-T excretion

beyond 5 days was estimated by extension of the excretion curves to zero
(to 15 days for the 16 and 32 aehg material and to 8 days for the 2 and
4 aehg material) and integration.

The assumption is that all the

2,4,5~T absorbed was excreted in this time period.

A reasonable

correlation was observed between the concentration of 2,4,5-T in spray
mixtures kept moist on skin and the amount of 2,4,5-T appearing in the
urine during five days post-treatment period, although it was not
strictly proportional (table 31).
Net absorption of 2,4,5-T per hour per square foot of skin exposed was
estimated from data in. table 31.
Concentration of spray
roatjgjrial^ __

_2j4,5-T absorbed (dermal^

aehg
2

0.220

4

0.419

16

0.570

32

1.125

It is emphasized these are niajidyia^ £p^ssJM£ vaj.ue^ because the skin was
saturated throughout the exposure period.

In actual practice these

levels will not normally be attained. The assumptions outlined above
and the dermal absorption data in table 31 (Newton 1978) were used to
calculate maximum applicator exposure for each of the 5 assumption sets
involving ground application (table 32) and the 5 sets involving aerial
application (table 33). These calculations indicate lightly clad
backpack sprayer, handgun sprayer, and backpack raistblower operators
will receive the greatest exposure.

Addition of a hat, gloves, and

long-sleeved shirt will markedly reduce exposure.

5-181

�a/

Table 31—Absorption and excretion of 2,4,5-T by humans after dermal exposure —

Concentration
of
spray mixture—

1

16
32

Ui

i—»
00
bo

Day
3

2

4

5

ag

lb/100 gal

2
4

Estimated 2,4,5-T

2,4,5-T recovered in urine

excretion in urine
beyond the 5th day
mg

0.073
0.218
0.116

0.142

0.107

0.250
0.222

0.134
0.124

0.276

0.358

0.250

Estimated
2,4,5-T
absorbed—
:

=g

0.025
0.079

0.034

0.062

0.441

0.037
0.095

0.125
0.500

083
.4

0.107
0.210

0.196

1.000

2.380

1.164

a/ Exposure involved 144 square inch denin patches soaked with 40 ml of 2,4,5-T spray solution of the
appropriate concentration and applied to the upper thigh. The patches were covered with plastic wrap
to prevent drying and were bound snugly to insure good contact with the skin. The skin was wet with
the spray mixture throughout the exposure period. Patches were removed after 2 hours, the skin washed
with alcohol and dried, and urine collected for 5-24 hour periods. 2,4,5-T excretion in urine beyond
the 5th day was estimated by extention of the excretion curves (to 15 days for the tiro highest
concentrations and to 8 days for the two lowest concentration) and integration. (Newton 1 7 )
98.
b_/ Acid equivalent per 100 gallon (aehg) .
cj

Estimated 2,4,5-T absorbed is the sum of 2,4,5-T excreted in five days and estimated excretion
beyond 5 days.

�Table 32—Sets of assumptions for exposure of applicators using 2,4,5~T with
ground equipment. Maximum levels of exposure are listed for each
assumption set because they assume constant wetness of exposed skin.
Dosage based on 60 kg worker except for the applicator monitored
data (80 and 110 kg).

Variable

1

2

Assumption set
3
4

Spray concentration,
aehg

4

8

16

Fully clothed^
Square feet of skin
exposed

No

Yes

No

Yes

Yes

No

2

I/A

2

1/4

1/4

2+

Dermal absorption
of 2,4,5-T mg/hr

088
.3^

O.U^

11^
.4

012
.4^

0 1 ^ 51-'
.5

2,4,5-T dosage,
mg/kg/hr

0.014

0.0018

0.019

0.0024

0.0025 0.85

TCDD dosage^ yg/kg/hr

8.4xlO~7 l.lxio"7

Applicator monitoring
mg/kg/day 2,4,5-T

16

"T"
400

PD-la
.40

1.14xlO~6 1.4xlO~7 l.SxlO*7 2.1xlO~5

0.026
(for 8 aehg)

0.0025
(for 6 aehg)

&amp;l Long-sleeved shirt and gloves reduces exposure 91 percent compared
to short-sleeve shirt and no gloves (Wolfe e.t al. 1974).
W Newton (1978).
£/ Norrls (1974) Based on absorption salts of organic arsenicale by Injector
operators using 6 Ib/gal concentrate, maximum concentration of 1 ppm In
urine with dally 6-hour exposure. The organic arsenlcals as salts are
better models for 2,4,5-T amine than is the 2,4,5-T ester used by Newton (1978).
d/ Value from PD-1 (EPA 1978).
—fl
e/ Based on 3slO ppm TCDD in 2,4,5-T (Alford 1978) and an absorption rate for
TCDD which is twice.as great as for 2,4,5-T. Thus yg TCDD absorbed » ng 2,4,5-T
absorbed x (6 x 10 )
.

5-183

�Table 33—Sets of assumptions for exposure of applicators using 2,4,5~T with aerial
equipment. Maximum levels of exposure are listed for each assumption
set because they assume constant wetness of all exposed akin.
Dosage based on 60 kg workers.

Variable

Spray concentration
aehg

_____
AesuiBgtion set_
_
6 ~"~ ~f— " f
—9-

10

40

10

__
-Jo"

40

40

40

Fully clothe^

Yes

Yes

Yes

Yes

No

No

Square feet of skin
exposed

1/4

1/4

1/4

1/4

2

2+

Inhaled 2,4,5-T, mg/hr

0

0

Skin deposit of
2,4,5-T, mg?"-'

~

-

1.042

2.084

Dermal absorption of
2,4,5-T mg/hr

0.125

0.371

0.052

0.104

0.834

0.75

Total exposure to
2,4,5-T, mg/hr

0.125

0.371

0.052

0.1041

0.8341

0.92

2,4,5-T dosage
mg/kg/hr

0.002

0.006

8x10

0.002

0.014

0.0103

TCDD dosage
7

&amp;
2.5x10"*" 1x10

Jj/

16.86

,

7
fi
1.2x10"' 3.7x10"°

R
5.2x10

7
1x10

7
8.3xlO~'

6.7x10

a/ Long-sleeved shirt and gloves for assumption sets 6 &amp; 7 reduces skin exposure 91
percent compared to short-sleeved shirt and no gloves. A broad brim hat is added
for assumption sets 8 and 9 (Wolfe et al. 1974).
b/ Assumes Inhalation rate of 0.1 yg/min per acre pound applied in adjacent
swath when air movement carries fine droplets into flagmen's position
(based on 20 rain/day exposure between 0 and 165 feet downwind from spray
swath, Akesson 1978).
£/ Value from PD-1 (EPA 1978)
d/ Value from table 30.
je/ Based on 3xlO~8 ppm TCDD in 2,4,5-T (Alford 1978) and an absorption rate for
TCDD which is twice as great as for 2,4,5-T. Thus -yg TCDD absorbed mg 2,4,5-T absorbed x (6 x 10 ).

5-184

�EXPOSURE MEASURED DURING OPERATIONAL APPLICATION

Lavy (1978b) monitored the deposition of 2,4,5~T on 22 applicators
engaged In the operational application of herbicide by helicopter (5
applicators), tractor-mounted boom sprayer (1 applicator), tractormounted mletblower (4 applicators), and backpack sprayer (12
applicators). Workers were actively involved with the application for
1.93 hours (helicopter), 1.08 hours (tractor boom sprayer), 4.08 hours
(tractor mistblower), or 3.0 hours (backpack sprayer). Patches (6 2
100 cm patches for each worker) were attached to the clothing on the
chest, back, both biceps, and both thighs. At the end of the spray
period the patches were removed and analyzed for 2,4,5-T. The
assumption is that the spray deposited on the. six patches was
representative of the spray deposited on exposed areas of skin.
Lavy (1978a) reported urine samples were collected from these same
workers but a complete report of the data is not yet available (January
15, 1979). Lavy (1978b) indicates, however, that it appears
approximately 4 percent of the 2,4,5-T estimated to be on the skin was
recovered in urine. Lavy's (1978b) data, recalculated to show
mg/kg/hour 2,4,5-T deposited on the skin and the amount of herbicide and
TCDD absorbed (exposure), are in table 34.
The levels of exposure from an actual operational application (table 34)
are substantially lower than those calculated from the laboratory
experiment (tables 32 and 33). When calculated to be. on a directly
comparable, basis in terms of concentration of spray and skin area
exposed, the following values were obtained from the two experiments:

5-185

�Table 34—Deposition and dermal absorption (exposure) of 2,4,5-T by humans during operational application.

Application
method

Worker
number

Skin
exposed

Deposition .
of 2,4,5-T-'

Absorption. .
of 2,4,5-T-'

Absorption
of TCDD^'

B2

1

Helicopter^
ti
••
«

2
3
4

n

5

0.294
0.294
0.173
0.294
0.294

ug_/k_g/hr_
0.0002
0.0003
0.0001

6.0 x 10"9

0.0003

1.8 x 10~8

0.0095

0.0004
0.0003

2.4 x 10"8
1.6 x 10~°

Average
d/

Tractor, boom™

6

d/
Tractor, raistblover™

0.294

0.042

0.0017

1.0 x 10— 7

7
8

0.294

0.050

0.0020
0.0014

1.2 x 10— 7

0.173

0.0005

3.0 x 10"8

O.OOU

6.6 x 1 '
08

0.0012

7.5 x 10-'8"
1.3 x 10

II

H

II

M

9

0.294

0.035
0.012

n

II

10

0.173

0.026

Average
e/

Backpack-'
"
ti
it
M
n

8.4 x 10"8

_7

11

0.294

0.054

12

0.294

0.373

0.0021
0.0149

13
14

0.294
0.294

0.281
0,299

0.0112
0.0120

15
16

0.294

0.615
0.676

0.0246

1.4 x 10"6

0.0271
0.0049
0.0011
0.0043
0.0081

1.6 x 10"6

n

17

it

18

11

19

it

20

ii

21

ti

22

0.294
0.294
0.294
0.294
0.294
0.294
0.294

0.123
0.027
01.
.07
0.202
0.197

0.0079
0.0300

0.749

Average
•
7
b/
£/
d/
e_/

1.2 x 10"8
1.8 x 10"8

004
.06
0.0072
0.0019
0.0070

0.0123

Data from table 5 (Lavy 1978b) adjusted to per hour basis.
4 percent of deposit
ag/kg/hr 2,4,5-T absorbed x (6 x 10 ), see footnote e, table 32 in chapter 5 of this report.
Concentration of 2 ,4,5-T In spray solution) 40 aehg
Concentration of 2,4,5-T In spray solution: 20 aehg

5-186

8.9 x 10"7
6.7 x 10"7
7.2 x 10"7

2.9 x 10~7
6.6 x 10"8
2.6 x 10"7
4.9 x Kf7
4.7 x 10~7
1.8 x 10~*
7.4 x 10"y

�Method
of application

Concentration of
____^_SE££Z_—.

Helicopter

a/
Exposure to; J^yS^T^
Laboratory,,
Field
,
l^SE^EilP^Jl!-"
Experiment—
mg/kg/hr-

40

Tractor

Backpack sprayer

0.0003

40

0.076

0.0012

20

raistblower

0.076
0.038

0.0123

•2/0.294 in2 exposed skin (3.28 ft2)
--From tables 32 and 33
-From table 34
This illustrates the maximum nature of the exposure calculated using the
data from the laboratory experiment where skin was soaked throughout the
exposure period.

In practice this level of exposure does not occur

except in rare instances where abnormally high, accidental exposure
occurs.

There are two cases of this type of exposure noted in tables 32

and 33.
The two spray workers who received substantial exposure to 2,4,5-T were
(1) one worker sprayed Texas mesquite with 8 aehg 2,4,5-T in diesel fuel
3 out of 5 days for 8 hours each day. Clothing was coveralls without
gloves.

(2) One worker in Oregon sprayed blackberry bushes with 6 aehg

2,4,5-T in water.
leather boots.

The sprayer hose broke and soaked the trousers and

The trousers and boots were worn for 4 hours before

washing up (Newton 1978).
&gt;&gt;

The Texas worker did not use gloves and his hands came in contact with
the solution and the concentrate.

The 80 kg Texas applicator

equilibrated at the level of 2.12 mg total absorption per 6 hour day,
for a dosage of 0.026 mg/kg/day.

This is half the predicted dosage

encountered with one-hour exposure under assumption set 3, table 32,
which most closely resembles his situation in the field but is based on
16 aehg spray mixture. This emphasizes the "maximum nature" of the
estimates in tables 32 and 33 which were derived from data in table 31.

5-187

�The Oregon applicator data in table 32 Indicated an uptake of between 3
and 4 mg 2,4,5-T from an exposure surface of 2 sq ft over a 4-hour
period (0.037-0.50 mg/sq ft/hr). Assuming partial drying and soaked
skin for 2 hours, this exposure is estimated to be the equivalent of 2
square feet for 2 hours (0.075 mg/sq ft/hr). This is slightly higher
than the rates shown for either the 4 or 16 aehg data in table 32. In
addition to the spill, however, the Oregon applicator reported a 3-hour
exposure the same day in which a leaky valve kept his spray-wand hand
wet constantly.

Under the circumstances, this observation was clearly

an extreme example under assumption set 3, table 32, corrected to 6
aehg.

Both the above observations suggest that the data In tables 32

and 33 give maximum estimates of exposure under the described
conditions.
It is unfortunate there is not a more adequate data base currently
available on dermal absorption of 2,4,5-T by applicators.

Lavy (1978a)

indicates data on 2,4,5-T and its relation to deposition on applicators
will be available for inspection by March 1, 1979.

There is another

study of applicator exposure to 2,4,5-T that is being planned by the
Cook College Agricultural Experiment Statment, Rutgers University, New
Jersey.

The study will be completely by June 1, 1980 (Norris et al.

1979).
EXPOSURE LEVELS IN THE FIELD

Personnel applying 2,4,5-T in the field are usually operating under
conditions reasonably close to one of the assumption sets - job
descriptions in table 30. The exposures for each type of application
listed below were estimated for the first hour of operation from tables
32, 33, and 34.

The following discussion of exposure opportunities in the various
commodity uses has been presented to show the level of exposure and area
treated for each worker hour. These may be expanded according to the
number of hours per day actual operator time.

Generally 2 values.are

given; one is the normal operational level as predicted by the data in

5-188

�up to 0.076 mg/kg/hr for each 60 acres treated (assumption set 7,
table 33).— Adding gloves and a long~sleeved shirt, the exposure would
be reduced to 0.007 mg/kg/hr even for a worst case of exposure based on
data of Wolfe et al. (1974) (table 35).
Ground Application with Tractor Mistblowers - Broadcast Treatment
Lavy (1978b) (table 34) reports tractor raistblower operators may be
exposed to 0.0012 mg/kg/hr 2,4,5~T under operational conditions. A
comparable assumption set for the worst case of exposure was not developed,
but is likely to be similar to that for the backpack sprayer (table 35).
Ground Application with Backpack Miatblowers - Broadcast Treatment; and
Backpack Sprayers and Tree Injectors - Individual Stem Treatment
No operational exposure data are available for workers using backpack
mistblowers. The similarity to backpack sprayers suggests the use of
those data. Lavy (1978b) (table 34) reports exposure for this group is
0.0123 mg/kg/hr 2,4,5~T under operational conditions. Worst case
exposure is illustrated from assumption set 3, table 32. Performance
rate of one acre per hour per applicator would lead to an exposure of
0.030 mg/kg/hr. If long-sleeved shirts and gloves are used (assumption
set 4) exposure is reduced to 0.003 mg/kg/hr in covering one acre.
Workers using injectors are described in assumption set 5, table 32.
Based on one-half acre treated per hour, a worker receives a maximum
dose of 0.032 mg/kg/hr (table 35).

I/ Sample calculation: 0.006 mg/kg/hg (assumption set 7, table 33) x
12.67 (to adjust exposed area from 0.25 square feet to 0.294 m') * 0.76
mg/kg/hr. The exposed-area correction factor is 1.58 to adjust from 2
square feet to 0.294 ra . Adding long-sleeved shirt and gloves reduces
exposure 91 percent or 0.076 mg/kg/hr x 0.09 » 0.007 mg/kg/hr.

5-190

�Table 35—Summary of hourly exposure to 2,4,5-T estimated by absolute method

Exposure situation

Area treated
per hour

acres

time exposed
per day

Reduced
operational ,
exposure—

Operational ,
exposure—

hours

_

___

Reduced
Maximum , maximum , ,
d/
exposure— exposure—

mrr /Irrr /ll T-

•-

Timber
Aerial

60

4

Backpack

1

4

0.0003
_
0.0123

0.00003
0.0011

Injection
Tractor mist blower
Backpack mist blower

0.5
6.5

4
4

0.0012

1

4

100-300
100-300
1

0.076

0.007

0.030

0.003

—
0.0001

0.032
0.030

0.003
0.003

0.0123

0.0011

0.030

0.003

4

0.0004

0.00004

0.095
0.0342/

0.0049
0.0028

0.0004
0.0003

0.016
0.007

0.009
003
.0^
0.001

20

4
6
4

20

6

Range and pasture
Aerial
mechanic
flagger (2)
Backpack
Tractor Boom spray

0.0006

Rights of way
Aerial-mixer
Backpack and handgun
Truck-mount
Backpack mistblower

0.25-1.25
1-10
0.25-1.25

0.0003
0.0123

0.00003

0.076

0.007

0.0011

0.003

0.00003
0.0123

0.000003
0.0011

0.030
0.011
0.037

1
1

0.0002

0.00002

0.063
004
.3^

0.006

1.3

0.0026

0.0002

0.007

6
6
6

0.001
0.003

Rice
Aerial
mixer-loader
flag person (2)
Tractor boom sprayer

80
80

5

003'
.0*
0.006

a/
b_/
cV

Calculated from Lavy (1978b) with 0.294 m exposed skin area (abort-sleeved shirt).
Calculated from Newton (1978) adjusted to 0.294 n exposed skin area.
Calculated from Lavy (1978b). Long-sleeved shirt and gloves reduces exposure 91 percent (Wolfe et al. 1974).

dy

Calculated from Newton (1978). Long-sleeved shirt and gloves reduces exposure 91 percent (Wolfe et al. 1974).

5-191

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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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                <text>&lt;strong&gt;Corporate Author: &lt;/strong&gt;USDA-States-EPA 2,4,5-T RPAR Assessment Team</text>
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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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                <text>&lt;strong&gt;Corporate Author: &lt;/strong&gt;University of Milan; Chair of Obstetric and Gynecological Pathology</text>
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