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Author
CorporatG Author

Kotchmar, George S,, Jr.
Flame, Incendiary, and Explosives Division, Air Force
Armament Laboratory, Eglin AFB, Florida
Metabolism of High Concentrations of the Organophosphorus Insecticide
Phorate Applied Foliariy to Selected Plant Species

Journal/Book Title
Year
MOIltll/Day

Color

February
n

54
Project No. 5066

Friday, January 05, 2001

Page 172 of 194

�AFATL-TR-71-22
THE METABOLISM
OF HIGH CONCENTRATIONS
OF THE O R G A N O P H O S P H O R U S INSECTICIDE
PHORATE APPLIED FOLIARLY
TO SELECTED PLANT SPECIES

PYROTECHNICS BRANCH
FLAME INCENDIARY, AND EXPLOSIVES DIVISION

TECHNICAL

REPORT AFATL-TR-71-22

F E B R U A R Y 1971

Approved for public release; distribution unlimited,

AIR FORCE ARMAMENT LABORATORY
AIR FOtCE SYSTIMS COMMAND • UNITED STATES AIM FORCE

EGLIN AIR FORCE BASE, FLORIDA

�The Metabolism
of High Concentrations
of the Organophosphorus Insecticide
Phorate Applied Foliarly
to Selected Plant Species

George S. K o t c h m a r , Jr., Capt, U S A F
Billy C. W o l v e r t o r t
E l i z a b e t h I. Soothe
Sandra M. L e f s t a d

Approved for public release; distribution unlimited,

�FOREWORD

The active Air Force project directly related to the information
discussed in this report is Exploratory Development Project 5066. Requests
for further detailed information or any comments on this report may be
referred to Air Force Armament Laboratory (DLI), Eglin Air Force Base,
Florida 32542.
Statistical analyses were performed by Booz-Allen Applied Research.
The use of trade names is for identification purposes only and does
not constitute endorsement by the United States Air Force.
This report has been reviewed and is approved.

r ^ ^ { t^ —~z—/- te
FRANKIN C. p M E S w i o n e l , USAF
KLI
Chief, Flame, Incendiary and
Explosives Division

�ABSTRACT

Gas chromatographic and enzymatic analyses (cholinesterase-inhibition
SthSr«re used to monitor the metabolism of the organophosphorus
insect dde 0,0-diethyl S-[(ethylthio)methyl] phosphorod thioate (Pforate)
Ippfied fofiarly to three economically important plants (Homestead tomato,
Siley sorg m" and Honey sorghum). The resulting data provided guide ines
in predicting toxicity and persistence of metabo ite residues £r high

^binr^r^ei^i^

Ice d'on ass plates located adjacent to treated Plants, indicated the
formation of toxic phorate metabolites was without the influence of
biological substrates within the plants. There were no statisticaljy
s gnificant differences with respect to the rate of increase of cholinesterl e- n ibition percentage values between the sorghum and glass plates,
the rate of formation of anticholinesterase oxidized metabolites was
predominantly through chemical oxidation on the leaf surface and not by
K enzymecatalysis, or at least, the oxidation occurred at_such a
ratfas tfmask the enzyme catalysis. The large droplet size in the
application^ phorate resulted in higher toxic residue values, especially
on the surface of the plant, than would normally be expected.

Approved for public release; distribution unlimited.

m
(The reverse of this page is blank)

��TABLE OF CONTENTS

Section

I
II

Title

Page

INTRODUCTION

1

EXPERIMENTAL PROCEDURES

4

MATERIALS AND METHODS

4

STATISTICAL ANALYSES

9

III

RESULTS AND DISCUSSION

12

IV

SUMMARY AND CONCLUSIONS

40

REFERENCES

43

�LIST OF FIGURES
Figure
1

Title

Page

Plant Metabolism Pathway of Phorate (Based on Reference
5)

2

Horse Serum Cholinesterase Inhibition Versus Concentration
of 0,0-Diethyl S-[Ethylsulfinyl)methyl] Phosphorothiolate..

8

3

Cholinesterase Inhibition of Homestead Tomato.....

13

4

Cholinesterase Inhibition of Wiley Sorghum

14

5

Cholinesterase Inhibition of Honev Sorqhum (Phorate Applied
in May)
15

6

Comparison of Percent Cholinesterase Inhibition for Three
Varieties of Plants.

17

7

Percent Cholinesterase Inhibition, Homestead Tomato

19

8

Effects of Passage of Time upon Percent Cholinesterase
Inhibition, Homestead Tomato

20

2

9

Percent Cholinesterase Inhibition, Wiley Sorghum

10

Percent Cholinesterase Inhibition, Honey Sorghum..

11

Percent Chlinesterase Inhibition, Wiley and Honey Sorghum.. 23

12

Effects of Passage of Time Upon Percent Cholinesterase
Inhibition, Wiley Sorghum(March) and Honey Sorghum(April).. 24

13

Percent Cholinesterase Inhibition, Wiley and Honey
Sorghum (May)

26

Effects of Passage of Time Upon Percent Cholinesterase
Inhibition, Wiley and Honey Sorghum (May)

27

14

21
22

15

Percent Cholinesterase Inhibition, Glass Plates

16

Comparison of Percentage Cholinesterase Inhibition for
Glass Plates and Wiley Sorghum

33

Comparison of Percentage Cholinesterase Inhibition for
Gl ass PI ates and Honey Sorghum

34

17

VI

32

�LIST OF TABLES
Table
I

II
III

Title

Page

Plant Parameters Employed With High Concentrations of
Phorate.

5

Efficiency of Extraction Technique for Phorate With Tomato
and Sorghum
6
Measurement Days by Species and Experiment.

10

IV

Gas Chromatographic Analysis for Phorate From Tomato
and Sorghum.

,,.

V

Average Percent Cholinesterase Inhibition, Homestead
Tomato

12

VI
VII
VIII
IX

Average Percent Cholinesterase Inhibition, Wiley
Sorghum (March) and Honey Sorghum (April).
Average Percent Cholinesterase Inhibition, Wiley
and Honey Sorghum (May).
Gas Chromatographic Analysis for Phorate from Glass
Plates and Sorghum.

"
?R

^

*'

Persistence of Phorate Oxygen Analog Sulfoxide Equivalent

in Sorghum.

™

vii
(The reverse of this page is blank)

��SECTION I
INTRODUCTION

The research reported in this study constitutes part of a program to
elucidate toxicological and ecological hazards associated with repetitive
aerial applications and spills of organophosphorus insecticides. Toxicological hazards may exist in plant foliage even after environmental
persistence studies determine the absence or safe level of the parent
insecticide. These hazards result from the conversion of the parent
insecticide to toxic oxidized metabolites. The rate of this conversion
determines the nature and magnitude of the toxic residues in the plant
tissues.
The use of organophosphorus insecticides is increasing because of their
wide spectrum of effectiveness (comparable to the chlorinated hydrocarbons)
and their short residual action in water, soils, and plants. Any accident
involving ultra-low-volume formulations of insecticides could result in
a per-unit-area concentration that would be detrimental to agronomic plants
because of unacceptable residue levels. For this reason, data relating
the tolerance of agronomic plants to repetitive aerial applications of
ultra-low-volume formulations of organophosphorus insecticides are of
interest to military pest control programs.
Guidelines were desired for predicting toxicity and persistence of
metabolite residues in plants after application of high concentrations of
the insecticide. Insecticides in or under considerations for the Air Force
inventory include malathion (dithiophosphoric derivative), naled (phosphoric
acid derivative), fenthion (thiophosphoric acid derivative with sulfide
linkage), and Dursban^(thiophosphoric acid derivative).
Phorate, 0,0-diethyl S-[(ethylthio) methyl] phosphorodithioate, was the
insecticide selected because it is a model compound containing oxidation
sites analogous to those found in sulfur-containing organophosphorus
insecticides. Its toxicity, expressed as an oral 105^ value,
is more tnan 100 times as great as the most toxic insecticide presently
used by the militaryO). Thus, persistence data on toxic metabloties
of phorate should provide a model system of maximum toxic residues on
foliage wnich should be unapproachable for insecticides presently used
by the military wnen applied at the same concentration. Furthermore,
previous studies^' ^» "&gt; ^J have elucidated the plant metabolism
pathway (Figure 1) of the insecticide along with solvent-partitioning
functions of phorate and its metabolites(2, 4).
Conclusive research data are not available concerning insecticide
pnytotoxicity; however, it is known tnat plant species exhibit a wide
range of tolerance to applications of organophosphorus insecticides ^»'t.

1

�(CH3CH20)PSCH2SCH2CH3

S

0

(CH3CH20)2PSCH2SCH2CH3

0
^^
II
I
*r
(CH3CH20)2PSCH2SCH2CH3

N.
0 0
X
11
*
(CH3CH20)2PSCH2SCH2CH3

(CH3CH20)2PSCH2SCH2CH3

Figure 1.

Plant Metabolism Pathway of Phorate
(Based on Reference 5}

The basis for this phytotoxic resistance or susceptibility is not clear.
The experimental procedure used in this study allowed an investigation
into the role performed by individual plant chemistries in metabolizing
organophosphorus insecticides.
Studies of the morphological effects caused by highly concentrated
foliar applications of mevinphos and methyl demeton on selected plant
species indicated that, in general, brpadleaf plants were more susceptible
to the insecticides than were grasses^ 7 /. Severe morphological injuries
were observed on soybean, cotton, and tomato plants one day after foliar
treatment, w h i l e seven days were required before comparable injuries were
noted on corn and sorghum. Coleman and Dean^°' found that resistance of
sorghum to methyl parathion was genetically controlled in their studies
with a resistant and a susceptible variety, Wiley and Honey, respectively.
Thus, differential phytotoxicity to organophosphorus insecticides can be
expected between plant species as well as w i t h i n a given species. Differences do occur in the rates of metabolism of insecticides in different
plant species. A study^) of the plant metabolism of Di-Syston® (dithioSystoxdD) and phorate indicated that the rates of a reaction may vary
slightly from one plant species to another and according to the stage of
growth, but the data obtained may be used as a guide to the relative
proportions of the metabolites present at intervals after application. In

�another study w y the effects of temperature and plant species upon the
rates of metabolism of systemically applied Di-Syston®were considered,
and s i m i l a r results were obtained. Phorate differs from Di-Syston® due
to the presence of an ethylene rather than a methylene group in its side
chain. Thus, this study attempted to relate the metabolism of the insecticide to phytotoxic damage among plant species and within a plant species.
Oxidation can increase both the water solubility and the anticholinesterase activity of organophosphorus insecticides^"'. The logical
approach for monitoring anticholinesterase compounds (toxic phosphorus
esters) formed during the metabolism of phorate was a cholinesterasei n h i b i t i o n method. Phorate alone is too weak an inhibitor to be detected
in micro amounts, but when applied to plants, it is very rapidly converted
to potent anticholinesterase agents. The final unhydrolyzed metabolite
(phorate oxygen analog sulfone) in the oxidation series (Figure 1) is
the most active i n h i b i t o r ' ^ ' . The 150 value (molarity of i n h i b i t o r which
results in 50 percent of the activity of the control) of phorate is
approximately 250 times that of the phorate oxygen analog s u l f o n e ' ^ ) .
One day after the application of phorate to corn, the residue of phorate
sulfoxide, which has an 159 value approximately 1/100 that of phorate,
was more than three times that of phorate^.

�SECTION II
EXPERIMENTAL PROCEDURES
1. MATERIALS AND METHODS
a. Apparatus. A Son/all Omni-mixer^ was used for macerating plants.
A gas chromotograph equipped with a flame photometric phosphorus detector
and a digital integrator was employed in the phorate analyses. A
recording pH stat was used to determine cholinesterase activity.
b. Reagents and Solvents. Standards, supplied by the American
Cyanamid Company, were technical grade phorate (Thimet® ) of 90-percent
purity, analytical grade phorate of 97.8-percent purity, and 94-percent
phorate oxygen analog sulfoxide containing 6-percent phorated oxygen
analog sulfone.
Reagents were anhydrous sodium sulfate, certified A . C . S . ;
acetylcholine perchlorate (a "rare and fine" chemical from K and K
Laboratories, Inc.); sterile filtered horse serum (Colorado Serum Co.);
sodium chloride (crystals), analytical reagent grade; sodium chloride
(granular), U.S.P. grade; sodium hydroxide pellets, analytical reagent
grade; and potassium hydrogen phthalate, certified A.C.S. acidimetric
standard.
Solvents were certified A.C.S, acetone, certified A.C.S. hexanes,
and vegetable oil.
c. Plant Parameters. The representative broadleaf plant selected
was Lycopersicon esculenturn mill, var. Homestead 24 (tomato), and the
grasses were Sorghum vulgare Pers. var. Wiley (sorghum), and Sorghum
vulgare Pers. var. Honey (sorghum). The two varieties of sorghum were
selected to represent a variety (Wiley) that was resistant to an organophosphorus insecticide and one (Honey) that was susceptible. The plants
were grown in a clear glass greenhouse with a minimum night temperature
of 60° to 65°F and a maximum day temperature of 95° to 100°F. Seeds were
planted in a soil consisting of a 7:3:1 mixture of sandy loam, peatmoss,
and perlite with four pounds of dolomitic limestone and one pound of
superphosphate added per cubic yard of soil. The pH of the soil was 6.5.
Each tomato plant was transplanted to an individual four-inch plastic pot
at the age of four weeks. The sorghum experimental unit consisted of 10
plants per four-inch plastic pot. A 15-15-15 liquid fertilizer was applied
bi-weekly.
A 2 percent or 1 percent solution of phorate (0.2 milliliter or 0.1
milliliter of technical grade phorate dissolved in 10 mi Hi liters of
vegetable oil medium) was applied foliarly as 0.01 milliliter droplets
with microsyringe to the tomato and sorghum at the concentrations shown
in Table I. This procedure allowed a uniform and exact application to all

�TABLE I. PLANT PARAMETERS EMPLOYED WITH HIGH CONCENTRATIONS OF PHORATE

Species

Age, Weeks

Homestead Tomato

Date of
Application
8 August1969
19 November 1969

Phorate, Concentration,
pprrr

lb/Ab

19,839
16,630

2.19
1.84

Wiley Sorghum

4
3

2 March 1970
20 May 1970

8,753
(c)

1.26
(c)

Honey Sorghum

4
3

8 April 1970
20 May 1970

8,461
(d)

1.22
(d)

Concentration of phorate solution based on gas chromatographic analysis
with analytical grade phorate.
"Concentration applied to plant based on leaf area (pounds of active
ingredient per acre).
c
Same concentration applied as 2 March 1970, but no gas chromatographic
analysis.
"Same concentration applied as 8 April 1970, but no gas chromatographic
analysis.
the plants. The levels of phorate applied were adjusted to the maximum amount
that would result in minimal visible damage. To insure similarity in
plant size at each application, the phorate was applied after three to
six weeks of initial plant growth. The varying lengths of time between
planting and insecticide application were to compensate for seasonal
variation in plant growth. Table I shows the age of the plants with the
date of application of phorate. During the March (Wiley sorghum) and April
(Honey sorghum) portions of the experiment, the phorate in the vegetable
oil medium was applied to glass plates located adjacent to the treated
and control plants.
d. Extraction Technique. The plants to be sampled were severed at
soil level, sectioned, and rinsed in a 400-milliliter beaker containing
25 mi 11 iliters of hexanes and 25 mi Hi liters of acetone in distilled
water (60 percent by volume) to remove any residues remaining on the
plant surface. The solvent mixture, followed with the plant material,
was poured into a cup for the Sorvall Omni-mixer®. The beaker was rinsed
with 5 mi 11iliters of hexanes and then by 5 mi 11iliters of acetone in
distilled water (60 percent by volume). After the plant material was
thoroughly macerated, the macerate was filtered through three layers of
5

�cheesecloth into a separatory funnel. The cup which had contained the
macerate was rinsed with 10 milliliters of hexanes and then by 10 millilitars
of acetone in distilled water (60 percent by volume). The rinsings were
added to the separatory funnel followed by 15 milliliters of a saturated
sodium chloride solution which aided in separating the organic and aqueous
phases.
Acetone was removed from the aqueous layer by use of a rotary evaporator attached to a water aspirator. Complete removal of the acetone
was essential because of its ability to inhibit cholinesterase. The
aqueous layer was filtered (to remove minute pieces of plant material)
through Whatman No. 2 paper into a 50-mi Hi liter volumetric flask and
brought to volume with distilled water. The organic phase was placed over
10 grams of anhydrous sodium sulfate, filtered into a 50-mi11iliter
volumetric flask, and brought to volume with hexanes. If the samples
could not be analyzed immediately, they were stored at 5°C.
The aqueous layer was analyzed for cholinesterase-inhibiting metabolites and breakdown products. Gas chromatographic analysis of the
organic phase for phorate allowed monitoring of the rapidity of breakdown and oxidation. The efficiency of the extraction technique, based
on the recovery of phorate in the organic phase, is shown in Table II.
TABLE II.

EFFICIENCY OF EXTRACTION TECHNIQUE FOR PHORATE WITH TOMATO
AND SORGHUM

Species

Date of
Experiment

Homestead Tomato

August
November

Wiley Sorghum

March

Honey Sorghum

Apri 1

Efficiency of Extraction, Percent
Controls3 Insecticide-Treated Plants^
3
3

66.2
87.7

32.4
63.2

63.3)
[ Qla ss
75.9) pla tesc

46.7

51 .7

^Concentration of phorate applied to plant placed through extraction scheme.
b
Phorate-treated plants from day 0 placed through extraction scheme.
c
Glass surface residues from day 0 placed through extraction scheme.
e. Cholinesterase-Inhibition Method. The advantages of using
cholinesterase-inhibition methods for determining organophosphorus residues
are that (a) the sensitivity is far greater than for chemical methods and
(b) the method is particularly suitable when the insecticide undergoes
6

�changes in the plant to produce metabolites with a high inhibitory
activity(10,11}_ One of the disadvantages is the lack of specificity
or inability to distinguish among different types of cholinesterase
inhibitors found within the plant.
The persistency of toxic metabolites and breakdown products in the
respective plant species was monitored using an automated pH stat method(12)
to determine cholinesterase activity. The cholinesterase inhibition for
each species and glass plate sample was measured immediately after the
application of the insecticide and on various succeeding days for one
month. Control plants were treated with only the corresponding amounts of
vegetable oil and were similarly measured. The experiment was repeated
for each species.
The cholinesterase activity of the prepared water sample was
recorded with a recording pH stat. A sample (0.2 milliliter tomato or
0.4 milliliter sorghum sample) was placed in a microbeaker containing
5 milliliters of a 0.154-molar saline solution (9.000 grams of analytical
reagent grade sodium chloride in 1000 mi Hi liters distilled water) and
0.5 milliliter horse serum. The microbeaker solution was heated to
37.5°C and adjusted to pH 8.0 prior to addition of 0.3 milliliter of the
cholinesterase enzyme substrate, 0.110-molar acetylcholine perch!orate
(0.675 grams crystalline substrate in 10 milliliters distilled water).
The titrant, 0.0100N sodium hydroxide.was standardized with 0.0100N
potassium acid phthalate (0.20423 grams acid in 1000 milliliters
distilled water).
Normal-activity curves (no samples added) and control-activity
curves (aqueous samples from control plants) were obtained prior to
measuring cholinesterase activity for the aqueous samples from phoratetreated plants. Cholinesterase inhibition of the phorate metabolites and
breakdown products was expressed as a percentage value obtained from a
ratio of cholinesterase activity (expressed in units of micromoles of
acetylcholine hydrolyzed per minute per milliliter of horse serum) of
the samples from the phorate-treated plants to samples from the control
plants. A second percentage of cholinesterase inhibition was calculated
using the normal activity value as the base.
f. Calibration Curve. To equate the percentage of cholinesterase
inhibition to the concentration of the metabolite extract, a log-linear
plot was made of the phorate oxygen analog sulfoxide equivalent, in
parts per million (ppm) of 0,0-diethyl S-[(ethylsulfinyl) methyl]
phosphorothiolate, versus the percentage of cholinesterase inhibition.
Figure 2 contains the calibration curve based on 0.4 milliliter samples of
the standard parts-per-million solutions of the phorate oxygen analog
sulfoxide. Sample sizes of 0.2 milliliter gave cholinesterase inhibition
percentages that were approximately half the values shown in Figure 2.

�109

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Figure 2.

30

50

60

HORSE SERUM CHOIIMESTERASE INHIBITION (PERCENT)
Horse Serum Cholinesterase Inhibition Versus Concentration of
0,0»Diethyl S-[(Ethylsulfinyl)methyl] Phosphorothiolate

�g. Gas Chromatographic Analysis. Gas chromatography was used to
detect unaltered phorate in the organic phase from the plant extracts.
A gas chromatograph equipped with a flame photometric phosphorus detector
was employed. A six foot by one-fourth inch stainless steel column
containing Chromport X X X , 80/90 mesh, coated with 3 percent SE-30, and
conditioned for 24 hours at 220°C, was used for the phorate analysis of
the August tomato extracts. A retention time of 105 seconds was recorded
with the inlet temperature set at 250°C, the column-oven temperature at
200°C, and the detector temperature at 235°C. Gas flow rates in cubic
centimeters per minute were nitrogen 80, hydrogen 150, air 20, and oxygen
20.
A six foot by one-fourth inch glass column containing Chromosorb id ,
80/90 mesh, coated with 3 percent QV-1 and conditioned for 24 hours at
210°C was used for the phorate analysis of the November tomato extracts,
March Wiley sorghum extracts, April Honey sorghum extracts, and glass
plates. A retention time of 130 seconds was recorded with the inlet
temperature set at 245°C, the column-oven temperature at 190°C, and the
detector temperature at 185°C.
Injection sample sizes 1 for August tomato extracts were 5 microliters,
and all others were 2.7 microliters. Concentrations of phorate present
in the August analysis were determined by integration of peak area by a
digital integrator. Concentrations of all other analyses were determined
by peak height. All determinations were expressed in parts per million
based on standard curves.
2.

STATISTICAL ANALYSES.

Before any of the data were analyzed, all of the cholinesterase inhibition percentages were transformed using the arc sine formula:
8 = 2 arcsin P
where 6 is the new variable to be analyzed
and P is the percent of cholinesterase inhibition divided by 100.
Tnis transformation minimized and stabilized the variation of the
data and created the homogeneity of variance that was essential to the
use of the analysis of variance technique, and the other statistical
procedures used for the analysis of these experiments. The results were
stated in percentage notations for presentation throughout the report.
It was not possiole to analyze all of the cholinesterase inhibition
percentages on an experiment-wide basis because the measurements of the
three experimental species were taken on various and differing days

�during the month following application of the insecticide. To make comparisons that were valid and meaningful, it was necessary to select those
days on which all species under consideration were measured. Table III
shows the days of measurement for each species. During the first week
TABLE III. HEASUREMENT DAYS BY SPECIES AND EXPERIMENT

Days After
Application

0
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
25
26
27

Homestead Tomato
August November

X
X
X
X
X
X

Wiley Sorghum
March May

Honey Sorghum
April May

X
X
X

X
X
X

X

X

X

X

X
X

X

X

X
X

X
X

X

X

X
X

X
X

X

X

X
X

X
X

X
X

X

X
X

X
X

X

X

X
X

X

X

X

X

X

X

X
X
X
X

X

X

X
X

X

X

X

X

X
X

X
X
X
X

following application of the insecticide, only those measurements that
were made on the same day were compared; during the next three weeks,
measurements that were made on contiguous days were also included in the
comparison.

10

�Only one measurement of cholinesterase inhibition was made on each of
the days for the Homestead tomato experiments and for the March and April
Wiley and Honey sorghum experiments. It was not possible, therefore, to
test for significance of the interaction between seasonal effects and the
number of days following application. Since this interaction would have
been used to test the seasonal and time-passage effects individually, an
unduly large interaction would have masked significance of the main effects,
Paired t-tests with the same or contiguous days' results were used to
circumvent this possibility. When nonsignificance of the paired values
was determined, an analysis-of-variance technique was used to test for
significance of the passage of time upon the cholinesterase-inhibition
percentage. In those cases in which these results were significant,
Duncan's new multiple range test was used to identify where the differences
did, in fact, exist. In the absence of significance, means were computed,
and the effects of the passage of time upon the cholinesterase inhibition
were studied. Two replicates of measurements were made for the May Wiley
and Honey sorghum plants, and it was, therefore, possible to use the
analysis of variance technique when only these data were involved in
comparisons.
Initially, all testing was conducted at the 95-percent probability
level (significant). When this proved significant, subsequent testing
was conducted at the 99-percent probability level (highly significant).

11

�SECTION

III

RESULTS AND DISCUSSION

Ultra-low-volume formulations of insecticides used by the military
involve the aerial application of a low-volume concentrate (0.75 to 10
ounces per acre, undiluted). Phorate is applied with normal formulations
at rates of 0.5 to 3 pounds of active ingredient per acre. Table I
presents the application rates within this range. However, the defined,
directed application of phorate to the leaf surface without spraying
resulted in a maximum interface between insecticide droplet (10 microliters)
and leaf area. This large droplet size represented the application of
high concentrations of phorate; the droplet contained more phorate (0.25
milligram) and is larger than that ordinarily found following routine
application of insecticides. The optimum3 diameter for insecticide spray
droplets is in the range of 20 microns'' '.
The percentages representing the efficiency of the extraction technique
employed (Table II) are minimum values because of the volatility of
phorate. Phorate is lost from the soil by volatilization and about 25
percent of the loss occurs in the first hour after treatment^'^/. Similar
results would be expected on the leaf surface, therefore, the length of
time between treatment and initial extraction of the plant would result
in a value of phorate present that is slightly less than that which was
applied. The time before initial extraction was approximately the same
in all cases; however, the extraction of the August tomato after application of phorate during the late morning heat probably accounts to some
degree for the lower value in extraction efficiency. Phorate was applied
to the other plants in the early morning.
A comparison of the percentage of cholinesterase inhibition obtained
using the normal-activity value and the percentage obtained using the
control-activity value as a base is shown in Figures 3 and 4 for Homestead
tomatoes and for Wiley sorghum for each of the two applications of
insecticide. A comparison for Honey sorghum is shown in Figure 5 for
the May application; however, the April control plants were not usable due
to contamination. The results of paired t-tests in analyzing the differences between percentages for each species allowed the use of all the
cholinesterase-inhibition percentages based on the normal activity value.
Cholinesterase-inhibition values obtained showed no correlation with
plant weight.
A comparison of the percentages of cholinesterase inhibition during
the month following application of the insecticide for each of the three
plants, using the analysis of variance technique, indicated that the
average for the Homestead tomato was significantly lower than those for

12

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TIME FROM APPLICATION WS)

a.

_

Phorate Applied in August

75

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18

20

22

1

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26

TIME FROM APPLICATION [VMS]
b. Phorate Applied _in November

Figure 3. Cholinesterase Inhibition of Homestead Tomato
13

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12 14 16 H 20
TIME FROM APPLICATION (PAKS)

22

24

26

28

1
26

21

a. Phorate Applied in March

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1
10

1
12

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14

1
16

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1
22

1
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TIME FROM APPLICATION

b. Phorate Applied in May
Figure 4. Cholinesterase Inhibition of Wiley Sorghum
14

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20

22

24

26

28

TIME FROM APPLICATIOW (PA^S)

Figure 5. Cholinesterase Inhibition of Honey Sorghum (Phorate Applied in May)

15

�the two varieties of sorghum. Figure 6 shows the inhibition percentage
values for each of the three plants; the lower level for the tomato
plants is evident. Therefore, for statistical purposes, data from the
tomato plant experiments were analyzed independent of the sorghum data.
Gas chromatographic analysis of the hexanes phase after extraction from
tomato and sorghum indicated less than one ppm phorate present by the sixth
day (Table IV). A determination of residues of-phorate and five of its netab-

TABLE IV. GAS CHROMATOGRAPHIC ANALYSIS FOR PHORATE FROM TOMATO AND SORGHUM

Day

Tomato
August November

Concentration of Phorate, ppm
Sorq lum
March (Wiley) April (Honey)

0

128

42

16

18

1

140

34

9-12

9

28

6-7

5-6

9

&lt;3

1

2
3

23

4

&lt;1

5

4

6

1

&lt;1

elites from various parts of corn plants (treated with one pound of the.insecticide per acre) indicated that phorate was essentially gone in 14 days(4).
During this determination, phorate was recovered from fortified samples with
96 percent efficiency using a Soxhlet apparatus in an eight-hour extraction
technique. The higher values of phorate in the August tomato samples, as
compared to the November samples, were due to the concentration of the sample
to 10 milliliters instead of the 50-milliliter final volume of all other
samples. Small differences in the data are probably due to the slight variations in extraction efficiencies for each plant. The disappearance of phorate
proceeds at approximately the same rate in each plant variety.

16

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HOMESTEAD TOMATO

,
0

1
2

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1
4

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8

O.VO I/EMBER

WILE/ SORGHUM

I3

•AUGUST
* MARCH

^ MA/

HO/JE/ SORGHUM
i
1 i
1
i
10
12

• APRIL
1
i
1
14
16

D MA/
t
1
20

i

1
IS

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TIME FROM APPLICATIO/V (3A/S)

Figure 6. Comparison of Percent Cholinesterase Inhibition
for Three Varieties of Plants

1
22

i

|
24

I
2&lt;

�The results of a cholinesterase-inhibition analysis for the Homestead
tomato plants for all of the days measured for the August and November
applications of insecticide are shown in Figure 7. An analysis of
comparable daily measurements in August and November indicated no significant differences between the two application dates or by the number of
days after application. The average percentages of cholinesterase inhibition for the days used in the comparison are given in Table V and Figure 8
and are not significantly different at the 95 percent probability level.
TABLE V.

AVERAGE PERCENT CHOLINESTERASE INHIBITION, HOMESTEAD TOMATO

Days After Application

Cholinesterase Inhibition, Percent

21,22

27.1

6

24.4

12,13

23.9

4

21.4

9,10

15.9

1

12.4

0

11.3

Figures 9 and 10 show the percentages of cholinesterase inhibition
for Wiley and Honey sorghum, respectively. Analyses of the possible
daily comparisons for each variety indicated significant differences
between the March and May data for the Wiley sorghum and highly significant differences between the April and May data for the Honey sorghum.
Similar analyses of those cholinesterase-inhibition percentages which
were obtained on the same or contiguous days for Wiley sorghum in March
and Honey sorghum in April indicated no significant differences between
the two varieties for those two months (Figure 11). An analysis of the
differences in cholinesterase-inhibition percentages with respect to the
number of days after application of phorate to sorghum during March and
April indicated highly significant differences. Table VI shows average
daily percentages. In Figure 12, the average values with associated
letters are shown graphically. The cholinesterase-inhibition percentage
peak was reached by the ninth day following application of phorate, and an

18

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AUGUST APPLICATIOM
WOI/&amp;MBER APPLICATION

70

72

74

16

18

TIME FROM APPLICATION (VAVS)
Figure 7. Percent Cholinesterase Inhibition, Homestead Tomato

O

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TIME FROM APPLICATION

Figure 8.

H

14

(VMS)

20

Effects of Passage of Time Upon Percent Cholinesterase
Inhibition, Homestead Tomato

24

26

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APPLICATIOW

JO
72
H
16
TIME FROM APPLICATION (VAVS]
Figure 9, Percent Cholinesterase Inhibition, Wiley Sorqhum

O

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APRIL APPLICATIOW
MAV APPLICATION

Figure 10.

O

TIME FROM APPLICATION {DAYS}
Percent Cholinesterase I n h i b i t i o n , Honey Sorghum

�95

WILEV SORGHUM
MARCH APPLICATION
HOWE/ SORGHUM
APRIL APPLICATION O

-25
10

72

14

U

TIME FROM APPLICATION (PA/S)
Figure 11. Percent Cholinesterase Inhibition, Wiley and Honey Sorghum

�Cxi
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TIME FROM APPLICATION
Figure 12. Effects of Passage of Time Upon Percent Cholinesterase
Inhibition, Wiley Sorghum (March) and Honey Sorghum (April)

�average peak level of 63.9 percent Inhibition was maintained until the
eighteenth to twenty-first day, when it began decreasing. By the twentythird to twenty-fifth day it had decreased to 31.5 percent.
TABLE VI.

Days
After
Application

AVERAGE PERCENT CHOLINESTERASE INHIBITION, WILEY SORGHUM
(MARCH) AND HONEY SORGHUM (APRIL)

Cholinesterase
Inhibition ,
Percent

Remarks (Common letter
indicates no significant
difference at 99-percent
Probability Level)

11

67.9

a

16,18

62.5

ab

9

61.1

ab

14

51.0

be

4

49.1

be

7

49.0

be

21,20

42.1

c

25,23

31.5

d

2

18.5

e

0

10.2

e

1

9.8

e

Figure 13 shows the percentages of cholinesterase inhibition for
Wiley and Honey sorghum on various days during May. The analysis
indicated highly significant differences only with respect to the
number of days after application; neither the species of sorghum nor
the species/day interaction yielded results which indicated any significant effect. The average percentages for the various days after application are shown in Table VII. All averages that are not significantly
different at the 99 percent probability level have a common letter.
In Figure 14, the average values with associated letters are shown
graphically. May Wiley and Honey sorghum plants reached a peak percentage

25

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n

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TIME FROM APPLICATION

Figure 13. Percent Cholinesterase Inhibition, Wiley and Honey
Sorghum (May)

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20

1

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TIME FROM APPLICATION (PAW)

Figure 14. Effects of Passage of Time Upon Percent Cholinesterase
Inhibition, Wiley and Honey Sorghum (May)

1

1
26

1

�of cholinesterase inhibition by the fourth day and maintained an average
peak level of 64.5 percent for the remainder of the month.
TABLE VII. AVERAGE PERCENT CHOLINESTERASE INHIBITION, WILEY AND HONEY
SORGHUM (MAY)

Days
After
Application

Cholinesterase
Inhibition,
Percent

Remarks (Common letter
indicates no significant
difference at 99-percent
Probability Level )

14

68.8

a

12

68.7

a

8

65.2

a

7

65.1

a

19

64.5

a

4

64.0

a

5

63.1

a

16

60.6

a

21

60.4

a

2

28.9

b

0

-1.5

c

With no significant differences existing between the two varieties of
sorghum in May or during continuous experiments in March and April, it
appeared that the metabolism of high concentrations of phorate proceeded
at the same rate in each variety; however, distinct visible differences
occurred between the two plant varieties.
Despite slight initial visible damage, both sorghum and tomato
recovered from insecticide damage within 30 days of treatment. The
preliminary data did show, however, that neither variety of sorghum
recovered from insecticide damage when exposed to the same concentration
of phorate as was used on the tomato plants. This is indicative of the
28

�effects of a high concentration of phorate due to the large droplet size,
since any visible damage at the rates used in this experiment would not
be expected. With the tomato, minor c u r l i n g of the leaves was observed
and many plants had a loss of apical dominance indicating that possibly,
at the concentrations of phorate used, there was a change in the auxin
content or hormonal distribution w i t h i n the plant. The first injury
symptoms for both sorghum varieties were characterized by a localized
bleaching of the blade pigments ( i . e . , chlorophyll) to a yellow-green
coloration with a s l i g h t l y flaccid condition. These necrotic blotches
were more distinct with Honey sorghum as they acquired a red-brown
coloration. This characteristic color difference was apparent in the
aqueous samples, as Honey samples were much darker than those of Wiley.
The flaccid condition was more evident with Honey sorghum. The more
v i s i b l e damage to sorghum compared to tomato in preliminary experiments,
with both exposed to the same concentration of phorate, may appear to
contradict the research reported in Reference 7. However, that report
notes that (a) conclusions regarding the possible effects of organophosphorus insecticides, except mevinphos and methyl demeton, could not be
made since the experiment was a fixed-effects model and not a random
selection of possible organophosphorus insecticides; and (b) differences
in plant response (susceptibility or resistance) could be accounted for
by a postulation that differences may be related to leaf area interception
of the insecticide.
The reason for existing differences between March/April and May
sorghum can only be postulated. Peak percentages of cholinesterase i n h i bition by the fourth day (64.5 percent) in May versus the n i n t h day
(63.9 percent) in March/April indicate a more rapid oxidation of phorate
to anticholinesterase metabolites. A s i g n i f i c a n t factor may be the
relatively higher mean temperatures in May. In an evaluation of the
effects of environmental temperature on Di-Syston©systemically applied
to cotton leaves, the oxidation of the s u l f i d e , Di-Syston®, to the
sulfoxide occurred so rapidly at temperatures above 70°F that only traces
could be detected, even at intervals as short as one hour after treatment'**)
The major^component in the leaves during the one-week experiment was the
Di-Syston®sulfoxide. The rate of disappearance of sulfoxide was increased
approximately 1.86 times for each 10°C rise in temperature (energy of
activation of 10 kcal/mole). The i n i t i a l oxidation of phorate in cotton
leaves was less rapid than the oxidation of Di-Syston®with traces of
phorate found up to three days, although these never.exceeded 5 percent
of the total radioactivity in the labeled experiment'^). It was also
noted^ that the rate of oxidation of the sulfoxides in the oxidation
series (Figure 1) was measurably slower for phorate than for Di-Syston®
The sum of the rate constants for the disappearance of phorate sulfoxide
due to oxidation is h a l f that of Di-Syston®sulfoxide. This indicates
that phorate sulfoxide was probably the major metabolite during the first
two weeks of this investigation. Also, when a l f a l f a seed was treated with
29

�treated with phorate or Di-Systorr% the effectiveness for aphid control
varied by as much as several weeks depending on the rate of plant grow
The rate of metabolism is slower in cooler weather, and the slower the
plant growth, the longer the persistence of toxic residues.
Tomato behaved similarly to the May sorghum. Tomato maintained a mean
percentage value of 19.5 throughout the experiment; sorghum maintained
a constant mean value throughout the month after, the third day.
Thus, the results indicated that the metabolism of high concentrations
of phorate proceeded at approximately the same rate in each species and
between plant varieties. These results were not in complete harmony with
those from earlier experiments. In previous metabolism studies of phorate
and Di-Syston®on various plants such as cotton, alfalfa, lemon, and bean,
it was found that the rates of reaction may be expected to vary slightly
among pjant species and according to the stage of growth^). Later,,
studies\°' specifically oriented toward the metabolism of Di-Syston^in a *
variety of plant species, indicated that at 70°F, the metabolism of Di-Syston
sulfoxide and hydrolytic decomposition of the toxic products occurred two
to three times faster in tomato leaves than in cotton leaves.
Differences in results and insecticide application parameters indicated
the experimental data resulted from the chemical nature of phorate on
the plant surface without the influence of biological substrates. Application methods^ 5 &gt; included topical application of 5 to 25 microliters of
insecticide to the base of a young plant or placement of isolated leaves
in a water dispersion (0.1 percent solution) of the insecticide to permit
the study of the rates of metabolism uncomplicated by the continual
accumulation of translocated material. The method of application used in
this work was foliar with a definite quantity of phorate aoplied as larae
droplets to each intact plant.
An earlier study' '^/ with Systox^(similar to phorate in structure)
showed that the chemical nature of the surface washes from fruit treated
with thiono- and thiolo-isomers changed rapidly upon exposure to light
and air. Exposure of the isomers to light and air under controlled conditions on glass plates, uncomplicated by biological substrates, resulted
in a surprisingly rapid conversion of the Systox®isomers into compounds
which appeared to be chromatographically similar to those found within
the plant tissues. Another study'''' showed that the action of air and
sunlight on surface residues of Systox®isomers has a rapid effect and
appears to promote their oxidation in the same sequence as found in vitro
with hydrogen peroxide and in plant tissues. Thin films of phorate
exposed to ultraviolet light or sunlight and air gave similar
results^» ^8, 19, 20) ^ Exposure to sunlight on paper, glass, and leaf
surfaces indicated that the initial stable residues of phorate may not be
the original compound or its simple oxidation products; prolonged exposure
resulted in the formation of more polar compounds^' 0 '. Results of ultra-

30

�violet irradiation of phorate on the surface of a liquid suggested that
the oxidation products are the sulfoxide and sulfone of the parent
compound, with the sulfone showing greater persistency and the s p]foxide
being in greater quantity during the early stages of irradiation''^» ^0).
To substantiate the concept that the experimental results in these
investigations were without the influence of biological substrates within
the plants, the same concentrations of phorate were applied to glass
plates as were applied to the treated plants. The glass plates were
located on the greenhouse bench adjacent to the control and treated plants.
This was done with Wiley and Honey sorghum, in March and April, respectively,
Table VIII shows a comparison of the gas chromatographic data for the
plants and glass plates. Within 48 hours, phorate could no longer be
detected on the glass plates; the same rapid disappearance was noted with
the plants—approximately one ppm detected after 96 hours.

TABLE VIII. GAS CHROMATOGRAPHIC ANALYSIS FOR PHORATE FROM GLASS PLATES
AND SORGHUM

Day

Phorate Concentration, ppm
March
Aoril
Wiley Sorghum
Glass Plates
Honey Sorghum Glass Plates

0

16

22

18

26

1

9-12

5-6

9

5

2

6-7

5-6

4

&lt;3

1
&lt;1

6

The cholinesterase-inhibition percentages obtained from the glass
plates for the March and April experiments (Figure 15) were compared with
the values obtained for the treated plants (Figure 11). The plots are
very similar, with the glass plate cholinesterase-inhibition values being
significantly higher on all days considered. However, most noteworthy
is that the data through the twentieth day following application exhibited
logarithmically linear trends (99 percent probability level) with no
quadratic tendencies for both the sorghum and glass plates in March and
April. The best-fitting straight lines have been plotted (Figures 16 and
17), and the equations for each of the lines are:
31

�99. Sr

hUJ
O

R3 •&lt;

UJ

(A)

ro

CO
UJ

CJ

I

UJ

o
CJ

25

O

*
Figure 15.

n

APRIL APPLICATION

u

TIME FROM APPLICATION (PAKS)
Percent Cholinesterase Inhibition. Glass Plates

�99.5

UJ
CJ

c*:

o •—
l~&gt; UJ
co

to
t"-t

3=

&lt;Z

50

*—»
UJ

CJ

SORGHUM, MARCH APPLICATION
O GLASS PLATES, MARCH APPLICATION

2

7
TIME FROM APPLICATION (PAVS)
(LOGARITHMIC SCALE)

Figure 16. Comparison of Percentage Cholinesterase Inhibition for
Glass Plates and Wiley Sorghum

I
24

29

�99.5

UJ
UJ
UJ
_J

t—1

I—

•&lt;
uj

II
UJ

kV)
UJ

o

• HONEV SORGHUM, APRIL APPLICATION
OGLASS PLATES, APRIL APPLICATION

I

I

I

I

4
7
3
TIME FROM APPLICATION (VMS)

(LOGARITHMIC SCALE)

Figure 17. Comparison of Percentage Cholinesterase Inhibition
for Glass Plates and Honey Sorghum

79

24

29

�Wiley sorghum, March

Y = 0.597 + 0.484 log (X + 1)

Glass plate, March

Y = 0.922 + 0.626 log (X + 1)

Honey sorghum, April

Y = 0.489 + 0.480 log (X + 1)

Glass plate, April

Y = 0.917 + 0.621 log (X + 1)

where Y is the arc sine transformation of the percent cholinesterase
inhibition
and X is the number of days after the application of phorate in vegetable
oil.
An analysis of comparison of the linear plots gave significant results.
The percentage of cholinesterase inhibition increased at the same rate
for both varieties of sorghum. The percentages of cholinesterase inhibition for Wiley and Honey sorghum increased at the same rate as did
those for the glass plates. The percent of variation explained by the
linear trend is as follows:

Wiley Sorghum

78.6

Glass Plate, March

89.3

Honey Sorghum

88.2

Glass Plate, April

92.4

The rate of formation of cholinesterase-inhibiting compounds appeared
the same between the glass plates and sorghum plants. It appeared that,
at least at high concentrations of phorate, formation of anticholinesterase
oxidized metabolites was predominantly through a chemical oxidation on the
leaf surface, and not plant enzyme catalysis. This took place at least
at such a rate as to mask enzyme catalysis. With low concentrations of
phorate within sorghum blades, methods similar to those described in
References 5 and 8 could distinguish any difference in the rates of
metabolism between the two varieties of sorghum.
The higher cholinesterase inhibition values for the glass plates,
(Figure 15) in comparison with the sorghum (Figure 11), can be attributed
to the higher extraction efficiency with the glass plates. However, the
phorate plant residue analysis by gas chromatography indicated the presence
of phorate 48 hours after it could no longer be detected in samples from

35

�the glass plates. Although the cholinesterase-inhibition analysis Indicates
the same rapid oxidation of phorate on leaf and glass plate, phorate could
be present witnin certain portions of the leaf, e.g., within stomatal pores,
and hence, within a potentially low-oxygen environment. This could explain
the gas chromatographic data. An examination of roots resulted in no
detectable cholinesterase inhibitors. Metabolism studies with lemon leaves
showed the presence of large amounts of intact Di-Syston® accompanied by
very slow conversion to other oxidative products(8). This suggested that
the oil-soluble esters were being protected from aqueous hydrolysis by the
oil content of the leaves. This was confirmed bv a radioautograph which
showed nearly all of the radioactivity from P^2 Di-Syston® translocated
into a lemon leaf is confined to the oil glands. A similar radioautograph
of Systox®-thiol-isomer translocated into lemon leaves showed that, most of
the radioactivity was located in the aqueous tissues of the plants^''.
These differences were correlated with the relative water solubilities of
the compounds, i.e., Di-Syston® 66 ppm and Systox®thipl-isonner 3900 ppm.
The water solubility of phorate was recorded as 85
With the rate of formation of cholinesterase inhibitors the same en
glass plates and sorghum leaf surfaces, the lower cholinesterase-inhibition
percentage values for tomato (Figure 6) are difficult to explain. The
values are lower than expected with tomato having received a concentration
of phorate double that received by sorghum. Since the gas chromatographic
data for tomato and sorghum agree, the distinct differences in cholinesteraseinhibition percentage values could have resulted from poorer efficiency in
recovering oxidized metabolites from tomato compared to sorghum. The
similarities in graphic plots for May sorghum (Figure 14) and tomato (Figure
8) would support this rationale.
Evaluation of the cholinesterase-inhibition percentage values with
the calibration curve resulted in values relating the concentration of
toxic residues present in and on the plant foliage. Fourteen days after
application of phorate to Honey sorghum in April, sample preparation of a
foliar rinse of the surface of the plant accounted for approximately 50
percent of the total cholinesterase inhibition of the plant. A lack of
detection of phorate within seven days indicated that residues of the
oxidized metabolites in sorghum occurred to a very large degree via
oxidation of phorate on the leaf surface, absorption within the leaf, and
possible translocation within the plant. This is not in agreement with
the previous studies presented in References 5 and 9. Other researchers have
postulated(S) that the relative rates of absorption and translocation of
phorate and Di-Syston® increased as the experiment proceeded because of the
formation of more water-soluble oxidative metabolites in the subcuticular
layers of olant tissue around the region of application. In Reference 9,
the postulation is that the parent compounds were fairly persistent on the
surface of the leaves but were metabolized rapidly once they had penetrated.

�These variations can be explained by the differences in application method
and in insecticide concentration: i.e., a 5 microliter topical application
to the base of the stem of a cotton plant versus a 0.2 milliliter application of a 2 percent solution of phorate in vegetable oil to the blades of
sorghum.
It must be remembered that as the toxic metabolites are forming, they
are concurrently being hydrolyzed to nontoxic phosphoric or thiophosphoric
acids. Though the oxygen-analogs of phorate can inhibit cholinesterase
activity more than their thionpohosphate precursors, they appear to have
a higher degree of instability'^' ^'• The phosphorus is considerably more
electrophilic in the P=0 compounds, thus weakening the P-S ester bond and
facilitating hydrolysis and accelerating phosphorylation of the enzyme'^).
Consequently, the presence of relatively large amounts of a highly oxidized
metabolite in a plant would result in higher cholinesterase inhibition and
higher apparent residue values than would an equivalent amount of a metabolite with less cholinesterase activity in another plant. The higher
cholinesterase-inhibition values mean the presence of metabolites which
are easily hydrolyzed, resulting in an overall faster rate of metabolic
detoxification.
The concentrations of phorate metabolites in tomato and sorghum were
expressed in parts per million (ppn.) as phorate oxygen analog sulfoxide
equivalent via a cholinesterase-inhibition method of analysis. The calibration curve for the residue method is given in Figure 2. It is independent of plant material analyzed and of the sample preparation technique.
It reflects none of the losses that may occur in the various steps of
sample preparation. A sample calculation follows the formula:
.v = parts per million of phorate oxygen analog sulfoxide equivalent
in sample analyzed.
Where w is the phorate oxygen analog sulfoxide equivalent obtained in the
analyses, micrograms.
v is the aqueous extract in the determination, mi Hi liters.
V is the total solvent in sample extraction, milliliters.
W is the sample extracted, grams (fresh weight).
The toxic residues present in tomato foliage were based .on the average
weight of tomato plants initially after application of phorate (six weeks)
and at the conclusion of the experiment (nine weeks), 6 grams and 28 grams,
respectively. Thus, residues in the tomato foliage ranged from 1.1 to 5.3
ppm phorate oxygen analog sulfoxide equivalent.

37

�Residue persistence in sorghum (Table X) was higher. The May sorghum
had concentrations with a range of 0 to 20.2 ppm. The average residue value
after the second day was 17.9 ppm. The March/April sorghum had concentrations with a range of 2.4 to 18.5 ppm. The fourfold increase in residues
by the ninth day is comparable to that found by Bowman and Casida'^' in
considering the persistence of phorate-P 2 and its metabolites in vegetable
crops. The total anticholinesterase activity of greenhouse pea plants,
sprayed with phorate at one pound per acre, increased for about the firslv
four days and then declined, but inhibitors persisted for 20 to 30
^ '
Foliage application of 0,0-diethyl S-[(isopropylthio) methyl] phosphorodithioate to pea plants resulted in the appearance of anticholinesterase
metabolites within one day and persistence of such metabolites in high
concentration for at least nine days with detectable amounts present for
21 days^'. The results of this investigation were comparable: the main
difference was higher residue levels.
In crops treated with phorate., the ultimate toxic residues are present
in a fractional part per million'". When applied to corn at a rate of one
pound per acre, phorate was essentially gone in 14 days, while very low
levels of its sulfoxide and sulfone (0.1 ppm or less) persisted through the
28-day experimental interval. At harvest time, the plant was essentially
4
free of insecticide, less than 0.01
'
The concentration of phorate metabolite residues present, though high,
would probably be at a safe level by harvest time. The ultimate toxic
metabolites present in harvest time residues are dependent upon both the
interval between application and harvest and the method of application.
Older plants having phorate applied at high rates would definitely have to
be monitored for toxic residues.
The lower residue values for tomato foliage are due in part to a
larger daily plant weight—approximately threefold that of sorghum. The
result could be a more rapid metabolism and hydrolysis and provides another
possibility for the cholinesterase-inhibition percentage values being lower
for tomato than for sorghum.
Generally, oxidation. in plants never increases the toxicity of an
application significantly^"'. However, the large residue values obtained
in this study indicate that the toxicity is increased considerably on the
surface of the plant when high concentrations are involved. A number of
researchers, in speculating upon potential residue problems after various
methods of treatment with systemic insecticides, have concluded that persistence curves should be 8
established on different crops grow under different
environmental conditions' '. Military application of insecticides at normal
rates results in residues which can be monitored with guidance from available
literature. Residue breakdown of these organophosphorus insecticides is
usually rapid with no persistency problems. However, the result of repetitive

38

�aerial application or spillage of insecticides in cropland areas may
result in concentrations higher than usual. This study indicates exposure
studies of the respective insecticides on glass plates alone under different
environmental conditions would serve as a guide in predicting residues from
high concentrations of insecticides.
TABLE IX.

PERSISTENCE OF PHORATE OXYGEN ANALOG SULFOXIDE EQUIVALENT IN
SORGHUM

Time From Application,
Day

0
1
2
4
5
7
8
9
11
12
14
16
18
19
20
21
23
25
a

Concentration, ppm
March /April 3
2.4-5.3
2.4-5.3
2.4-5.3
10.3-14.5
10.3-14.5

Mayu

0
8.3
17.1
19.7
18.7
18.5

12.6-18.5
16.0-18.5
10.3-14.5
12.6-18.5
12.6-18.5

16.6
20.2
18.0
15.3

10.3-11.9
10.3-11.9
6.9-7.9
6.9-7.9

17.0

Concentration range is the result of considering the standard deviation
for the average plant weight for the entire experimental period in May;
this is due to the lack of plant weight values for March/April. Results
are averages of two samples, three replications each.

3

Results are averages of four samples, three replications each.

39

�SECTION IV
SUMMARY AND CONCLUSIONS

Data on the metabolism of foliar applications of high concentrations
of the organophosphorus insecticide phorate on Homestead tomato and Wiley
and Honey sorghum are reported. The investigation of phorate metabolism,
monitored by gas chromatographic and enzymatic analysis, produced the
following results:
1. The cholinesterase activity values obtained showed no correlation
with plant weight.
2. The disappearance of phorate appeared to proceed at the same rate
in each plant species and variety; phorate disappeared more quickly from
glass plates than from March/April sorghum under the same experimental
parameters.
3. No significant differences were apparent between the two varieties
of sorghum in May or during continuous experiments in March and April.
It appeared that the formation of anticholinesterase metabolites, after
high foliar applications of phorate, proceeded at the same rate in each
variety although distinct visible differences occurred between the Wiley
and Honey sorghum.
4. The peak percentages of cholinesterase inhibition from sorghum
samples by the fourth day in May versus the ninth day in March/April
indicated more rapid oxidation of phorate to anticholinesterase metabolites
at higher temperatures.
5. The phorate metabolism in tomato was similar to metabolism in the
May sorghum; however, actual comparison of percentage values of cholinesterase inhibition during the month for each of the three plants indicated
that the average for the Homestead tomato was significantly lower than
those for the two varieties of sorghum.
6. The percentage values of cholinesterase inhibition for the Wiley
and Honey sorghum increased at the same rate as for the glass plates,
indicating that the rate of formation of anticholinesterase-oxidized
metabolites was predominantly through chemical oxidation on the leaf
surface and not by plant enzyme catalysis; this surface oxidation took
place at least at such a rate as to mask enzyme catalysis.
7. The larger droplet size in application technique resulted in
higher toxic-residue values for phorate metabolites, especially on the
surface of the plant, than would normally be expected.

40

�This study was initiated to find a basis for predicting toxicity and
persistence of metabolite residues in plants after application of high
concentrations of sulfur-containing oraanophosphorus insecticides during
military spray operations. The results indicate that exposure studies of
high concentrations of insecticides on glass plates alone, under different
environmental conditions, would serve as a guide in predicting residues
from repetitive aerial application or spillage of insecticides used by
the military in cropland areas. Such studies with a controlled environment
would yield toxic-residue-persistence data under various conditions for
high concentrations of insecticides.

41
(The reverse of this page is blank)

��REFERENCES

1.

Thomson, W.T. Agricultural Chemicals, Book I. Insecticides,
Acaricides, and Ovicides. Thomson Publications, Davis,
California, 1967.

2.

Bowman, J.S. and J.E. Casida. Metabolism of the Systemic
Insecticide 0,0-Diethyl S-Ethylthiomethyl Phosphorodithioate
(Thimet) in Plants. J. Agr. Food Chem. 5: 192-197, 1957.

3.

Bowman, J.S. and J.E. Casida. Further Studies on the Metabolism
of Thimet by Plants, Insects, and Hammals. J. Econ. Entomol.
51:838-843, 1958.

4.

Bowman, M.C., M. Beroza, and J.A. Harding. Determination of Phorate
and Five of Its Metabolites in Corn. J. Agr. Food Chem.
17:138-142, 1969.

5.

Metcalf, R.I., T.R. Fukuto, and R.B. March. Plant Metabolism of
Dithio-Systox and Thimet. J. Econ. Entomol. 50:338-345, 1957.

6.

Coleman, O.H. and J.L. Dean. Inheritance of Resistance to Methyl
Parathion in Sorgo. Crop Sci. 4:371-372, 1964.

7.

Wolverton, B.C., W.J. Wallace, A.L. Young, and D.D. Harrison.
Studies on the Systemic Uptake of Toxic Phosphorus Esters by Plants.
Morphological Effects of Foliar Applications of the Organophosphate
Insecticides Mevinphos and Methyl Demeton on Selected Plant Species.
Air Force Armament Laboratory Technical Report AFATL-TR-69-116,
Eg!in Air Force Base, Florida, September, 1969.

8.

Metcalf, R.L., H.T. Reynolds, M. Winton, and T.R. Fukuto.
Effects of Temperature and Plant Species upon the Rates of Metabolism
of Systemically Applied Di-Syston. J. Econ. Entomol. 52:435-439,
1959.

9.

Heath, D.F. Metabolism in Plants and Soils. Jm Organophosphorus
Poisons, Anticholinesterases and Related Compounds edited by
D.F. Heath. Pergamon Press, Mew York, 1961.

10. Archer, T.E. Enzymatic Methods. Jm Analytical Methods for
Pesticides, Plant Growth Regulators, and Food Additives, Volume I
edited by G. Zweig. Academic Press, New York, 1963.
11. Sutherland, G.L., P.A. Giang, and T.E. Archer. Thimet. I_n
Analytical Methods for Pesticides, Plant Growth Regulators, and
Food Additives , Volume II edited by G. Zweig. Academic Press,
New York, 1964.
43

�12. Nabb, D.P. and Florence Whitfield. Determination of Cholinesterase
by an Automated pH Stat Method. Arch. Environ. Health. 15:147-154,
1967.
13. Himel, C.M. The Optimum Size for Insecticide Spray Droplets.
J. Econ. Entomol. 62:919-925, 1969.
14. Young, A.L. and B.C. Wolverton. Military Herbicides and Insecticides. Air Force Armament Laboratory Technical Note
AFATL-TN-70-1, Eglin Air Force Base, Florida, January, 1970.
15. Reynolds, H.T., T.R. Fukuto, R.L. Metcalf, and R.B. March.
Seed Treatment of Field Crops with Systemic Insecticides.
J. Econ. Entomol. 50:527-539, 1957.
16. Metcalf, R.L., R.B. March, T.R. Fukuto, and M.G. Maxon. The
Nature and Significance of Systox Residues in Plant Materials.
J. Econ. Entomol. 48:364-369, 1955.
17. Fukuto, T.R., R.L. Metcalf, R.B. March, and M.G. Maxon. Chemical
Behavior of Systox in Biological Systems. J. Econ. Entomol.
48:347-354, 1955.
18. Cook, J.W. and R. Ottes. Note on the Conversion of Some
Organophosphate Pesticides to Less Polar Compounds by Ultraviolet
Light. J. Assoc. Offie . Agr. Chemists. 42:211-212, 1959.
19. Mitchell, T.H., J.H. Ruzicka, J. Thomson, and B.B. Wheals.
The Chromatographic Determination of Organophosphorus Pesticides.
Part III. The Effect of Irradiation on the Parent Compounds.
J. Chromatog. 32:17-23, 1968.
20. Ruzicka, J.H., J. Thomson, and B.B. Wheals. The Gas Chromatographic
Examination of Organophosphorus Pesticides and Their Oxidation
Products. J. Chromatog. 30:92-99, 1967.
21. Metcalf, R.L., R.B. March, T.R. Fukuto, and M.G. Maxon. The
Behavior of Systox-isomers in Bean and Citrus Plants. J. Econ.
Entomol. 47:1045-1055, 1954.

44

�DISTRIBUTION LIST
AFSC (DLSW)
(SDWM)
(SGP)
ARPA (TECH INFO)
DDR&amp;E (CHEM TECH)
(TECH LIB)
SAAMA (SFQT)

2
3
3
1
1
5
5

AIR UNIVERSITY LIB
HQ DA OACSFOR (FOR CM SR)
OPERATIONS RSCH GRP
EDGEWOOD ARSENAL
(SMUEA-TD-S)
(SMUEA-RPRE (2))
(SMUEA-CC)
(SMUEA-QS)
(SMUEA-CCCR)
(SMUEA-TSTI-L)
(SMUEA-D)
(SMUEA-TS-CF)

1
1
1
1
2
1
1
1
1
1
1

(WPNS DEV &amp; ENGR LABS)
ENGR R&amp;D LABS (TECH DOC CTR)
ABERDEEN PRV GD (TECH LIB)
DESERET TEST CENTER (TECH LIB)
CBR AGENCY (CSGSB-ST)
USA CHEMICAL SCHOOL (AJMCL-A)
NAV AIR SYS COMD (AIR-532G)
USN WEAPONS LAB

2
2
1
4
1
1
2
2

USN RESEARCH LAB (CODE 6140)
4525 FTR WPN UG (FWOA)
6570TH AMRL (HEF)
DDC
12AF (DMEME)
DL
DLIP
SSLT
TAWC (DOD)
(DIM)
SOC (DFS)
HQ USAF (AFRDPA)
TAC (DOO-S)
SOF-DOR
319SOS-DM
TAWC-CB
USAFETAC
USAF ENVIRONMENTAL HEALTH LAB
(Kelly AFB TX)

1
1
1
12
1
1
50
2
1
1
1
2
2
2
2
1
1
1

45

�DISTRIBUTION LIST (Concluded)
USAF ENVIRONMENTAL HEALTH LAB
(McClellan AFB CA)

1

USAFEL
AFWL (DEE)
USAFA (DFLS)
DUGWAY PROVING GROUND (TECH LIB)
ONR (CODE 440)
HQ USACDC (NBC BRANCH)
ASD (ENYS)
DLOS
CDCLNO

1
2
2
1
1
1
1
1
2

46

�UNCLASSIFIED
Security Classification
DOCUMENT CONTROL DATA - R &amp; D
(Security classification of title, body of abstract and indexing annotation must be entered when the overall report is
ORIGINATING A C T I V I T Y (Corporate author)

Flame, Incendiary, and Explosives Division
Air Force Armament Laboratory
Eqlin Air Force Base, Florida
3

classified)

. REPORT SECURITY CLASSIFICATION

UNCLASSIFIED
26. GROUP*

REPORT TITL.E

THE METABOLISM OF HIGH CONCENTRATIONS OF THE ORGANOPHOSPHORUS INSECTICIDE
PHORATE APPLIED FOLIARLY TO SELECTED PLANT SPECIES
D E S C R I P T I V E NOTES (Type- ot report and inclusive dates)

Final Report (May - December 1970)
5 AUTHORCSI (First name, middle initial, Imxt name)

George S. Kotchmar, Jr., Capt, USAF3 Billy C. Wolverton, Elizabeth.E. Boothe,
Sandra M. Lefstad
6

REPORT D A T E

7«. T O T A L NO. OF PAGES

February 1971
8«- C O N T R A C T OR G R A N T NO.

&amp;. PROJECT NO.

5066

53

\7t. NO. OF REFS

1

21

9a. ORIGINATOR*^ REPORT NJUMBERfSt

AFATL-TR-71-22
9b. OTHER REPORT NO (si (Any other numbers that may oe assigned
this report)

C.

d.

1O. DISTRIBUTION S T A T E M E N T

Approved for public release; distribution unlimited.

M- S U P P L E M E N T A R Y NOTES

Available in DDC

12- SPONSORING M I L I T A R Y A C T I V I T Y

Air Force Armament Lauoratory
Air Force Systers Command
Eglin Air Force Base, Florida 32542

ABSTRACT

Gas chromatographic and enzymatic analyses (cholinesterase-inhibition method)
were used to monitor the metabolism of the organophosphorus insecticide 0,0diethyl S-[(ethylthio)methyl] phosphorodithioate (phorate) applied foliarly
to three economically important plants (Homestead tomato, Wiley sorghum, and
Honey sorghum). The resulting data provided guidelines in predicting toxicity
and persistence of metabolite residues for high concentrations of insecticides
employed by the military. An attempt was also made to relate the metabolism
of the insecticide to phytotoxic damage among and within plant species. The
data indicated that no plant-variety-dependent distinction exists in the
formation of toxic phorate metabolites as shown by in vitro anticholinesterase
activity recorded over a four-week period. Further investigation, with the
same high concentrations of phorate placed on glass plates located adjacent
to treated plants, indicated the formation of toxic phorate metabolites was
without the influence of biological substrates within the plants. There were
no statistically significant differences with respect to the rate of increase
of cholinesterase-inhibition percentage values between the sorghum and glass
plates; the rate of formation of anticholinesterase oxidized metabolites was
predominantly through chemical oxidation on the leaf surface and not by
plant enzyme catalysis, or at least, the oxidation occurred at such a rate
as to mask the enzyme catalysis. The large droplet size in the application
of phorate resulted in higher toxic residue values, especially on the surface
of the plant, than would normally be expected^

DD

FORM
1 NOV 65

1473

UNCLASSIFIED
Security Classification

�UNCLASSIFIED
Security Classification
1

14.

K EY

LINK A

LINKS

LINK' C

WORDS
ROLE

WT

ROLE

WT

Phorate
0,0-diethyl S-[(ethylthio)methyl] phosphorodithioate
Organophosphorus Insecticides
Plants
Insecticide Residues
Insecticide Metabolism

UNCLASSIFIED
Security Classification

ROL E

W T

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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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