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                    <text>Item ID Number

°1186

Author

Adamovic, V. M.

Corporate Author
Lower

Level Phenomena of DDT Cumulation in Female
Abdominal Fatty Tissue

JOIirnal/BOOk Title

Year

Arhiv za

Higijenu Rada

1973

Month/Day
Color
Number of Images

n

4

Alvin L. Young filed this item under the category
"DDT/Human Toxicology and Environmental Fate"

Wednesday, April 11, 2001

Page 1186 of 1242

�hig. rada. 24 (1973) 303.

LOWER LEVEL PHENOMENA
O F JJDJ C U M U L A T I O N I N F E M A L E
ABDOMINAL FATTY T I S S U E f

^-V. M. A n fl M n v i ^ and B o R K A S O K I d
Institute for Health Protection of Serbia, and Department for Sanitary
Chemistry, Beograd
The authors found a significantly higher level of DDT storage
in the fatty tissue samples of men than in women (mean pp'DDE
was 12.8 ppm and 10.2 ppm respectively). By comparing the excretion of organochlorine insecticides in the milk of breast-feeding
mothers with their total daily DDT intake by food, they registered
considerably greater quantities of pp'DDE eliminated than ingested. By excluding the nondietetic DDT intake the authors explain
this phenomenon by hormonal factors i. e. by increased mobilization of the stored DDT metabolites during the lactation period.
The lower DDT storage found in women may also reduce the mean
residue values related to the general population.
Irrespective of its restricted use the presence of DDT in the human
environment will continue for some time yet to influence to a very great
extent man's existence and of course, his health. The conclusions arrived
at meetings of experts (1) show that DDT will continue to be used for
controlfing the vectors of certain diseases and even in the control of
various agricultural pests. Taking into account the persistence of these
compounds on one side and the quantities that have been used so far
and that will be used in the future on the other, it is not hard to conclude that man's contact with DDT remains inevitable, whatever guarantees may be prescribed.
Past investigations of the toxioological, cancerogenic, mutagenic and
other properties of DDT have yielded so many data that it may well be
claimed that DDT is the most widely checked compound to date (2, 3).
Even so, present knowledge does not offer a realistic idea of its effect
upon man. Very little is known about the daily effect of small quantities
"Of DDT on the general population, except that it is stored in the adipose
'tissue (4) and that it is thus present in all organs of vital importance.
These effects can be evaluated by periodical determinations of the concentration of stored DDT and its degraded products in the human adipose tissue and blood or serum, and correlated with the data on the

�304

V. M. AlMMOVld, BORKA SOKI(5

daily intake of DDT with food. Some authors have found the concentration of stored DDT to be on a steady downward line and it is considered that the measures undertaken will further diminish its excretion (2).
Among numerous data of this kind there are some which suggest the
existence of a significantly higher level of DDT, especially of pp'DDE,
in males than in females. We found the same in 1967/68 after having investigated 100 samples of adipose tissue from the inhabitants of Belgrade and Serbia proper (5): the mean value of the total DDT depot was
10.2 ppm in women as compared to 12.8 ppm in men, the total mean
value for the general population amounting to 11.5 ppm.
This difference of about 2—2.5 mg/kg of adipose tissue is to be found
in papers published before (6) and after (7, 8) our report, although there
have been papers (9) in which no difference was found. The existence of
a difference has been explained in several ways, one being the relative
complexity of female hormonal interrelationships which could conceivably result in an increased microsomal enzyme activity and a subsequent
body burden reduction. This may also be interpreted in part by a differing female pattern of fat deposition and the likelihood of males having
greater environmental exposure to pesticides. However, in the course
of our examinations of the factors contributing to increased concentrations of organochlorine insecticides in infants (10) we found some interesting data which might help to explain this phenomenon too.
Namely, in investigating the daily intake of organochlorine insecticides by infants we also determined the entire daily intake of these insecticides with food by breast-feeding mothers and the daily excretion
with milk. We found a significant disproportion between the total daily
intake of DDT and its excretion as illustrated in Table 1.
From the above data the following may be concluded:
a) breast-feeding mothers excreted considerably greater quantities of
pp'DDE with milk than they took in with food;
b) the disproportion was far greater in mothers of twins (A and B)
than in mothers of a single child (persons C);
c) similar occurrences were not found in the case of other organochlorine insecticides, although we found (5) that the levels of stored
djeldrin likewise differed according to sex, which was not suggested by
other authors.
Since the experiment was carried out under controlled conditions and
since the factor of non-dietetic DDT intake could be ignored on this
occasion, obviously a powerful mobilization of the stored pp'DDE and
other DDT derivatives takes place during the lactation period i, e., the
surplus of DDE excffeted with milk becomes more apparent. Knowing
that the »good old practice* of breast-feeding is still maintained in some
parts of the world, that in some regions this lactation .period lasts up to
six — nine months, that a balance in subsequent storage of DDT is not

�LOWER LEVEL

PHENOMENA OF DDT

CUMULATION

305

Table 1
Total daily excretion of organochlorine insecticides in human milk compared
to their total daily intake with food (expressed in y/day person)
O

Person

Mean
quantity
of milk
ml/day

ffi
«

£
G,

CJ

ffl
«

W
Q
O

I

&lt;

Kj
O

&amp;

a

H
Q
Q

a

H
Q
Q

«

01

a.
o

5H
oQ
HQ

.s
•a

S

A

1.590

8

22

828

16

154

9

1.078

9

B

1.249

3

14

745

14

179

9

1.033

3

C

527

1

4

67

3

25

2

105

&lt;1

9

317

65

20

112

59

266

9

Total daily intake
with food (2.660 g)

The result represents the mean value for the observed period of seven consecutive days.
A and B are mothers breast-feeding twins
C are mothers with one child.
attained at once and that such cases figure among the examined subjects from the general population, we may assume that such samples
can significantly contribute to a decrease of the mean value for one group
of examined subjects and thereby explain the phenomenon of reduced
storage of DDT in women. This should be borne in mind when assessing the results of epidemiological studies of OC insecticide exposure.
References
1. Deichmann, W. B,: Arch. Toxikol., 29 (1972) 1.
2. Report of the Secretary's Commission on Pesticides and Their Relationship to Environmental Health. U.S. Dept. of Health, Education and Welfare, 1969.
3. Kagan, Yu. S., Pudel-Ossipova, S. I., Khaikina, B, J., Kuzminskaya, U. A.,
Kouton, S. D.: Res. Rev., 27 (1969) 43.
4. Howell, D. E.: Proc. Okla. Acad. Sci., 29 (1948) 31.
5. Adamovit, V. M., Hus, M.t Sindjic, M., Dukid, V.; Hrana i ishrana, 11 (1970)
6. Zavon, M. R., Hine, H. C., Parker, E. D.: J.A.M.A., 193 (1965) 181.
7. Watson, M., Benson, W. W., Gabica, J.: Pestic. Monit. J.( 4 (1970) 47.
8. Wyltie, /., Gabica, J., Benson, W. W.: Pestic. Monit. J., 6 (1972) 84.
9. FiSerova-Bergerova, V,, Radomski, J. £., Davtes, J. E., Davies, J. H.: Ind.
Med. Surg., 36 (1967) 65.
10. Adamovic, V. M., Soktt, B., Petrovic, O.: Ernahrungsforschung, 16 (1971)
579.

�306

V. M. ADAMOVIC, BORKA SOKI&lt;;

SaZetak
POJAVA MANJE KUMULACIJE DDT-ja U ABDOMINALNOM
MASNOM TKIVU 2ENA
Autori su naSli znacajno viSu razinu pdlaganja DDT-ja u masnom tkivu muSkaraca nego onorn u zena (srcdnja vrijednost pp'DDE iznosila je 12.8 ppm za
muSkarce odnosno 10.2 ppm za zenc). Usppredujuci izlucivanje organoklornih
insckticida u mlijeku zcna-dojilja s kolicinom DDT-ja uncsenog hranom, izmjerili su znatno viSe eliminiranih rezidua no 5to bi odgovaraio ingestiji insekticida. Isklju£ivSi drugi put apsorpcijc izuzev hranom, autori tumafie tu
pojavu hormonskim ciniocima, tj. povecanom mobilizacijom deponiranih metabolita DDT-ja za vrijcine laktacijskpg razdoblja. Smanjeno odlaganje DDT-ja
u zena bit cc da utje(?.e i na srednje vrijcdnosti deponiranih metabolita za
cjelokupnu populaciju nckog podrucja.
Odjel sanitarne kernije,
Zavod za zaStitu zdravlja Srbije,
Beogmd

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                    <text>Item ID Number
Author

Brown, Marry D.

Corporate Author
Final

Report/Article TltlB

Report: Herbicide (2,4-D) Applicator Exposure
Measurements

Journal/Book Title
000

Year

°

Month/Day
Color

n

Number of Images

48

DBSCrlptOn Notes

Supported by USDA Agreement No. USDA-TPSU-RU-0191 and New Jersey Agricultural Experiment Station
Project No. NJ04502.

Tuesday, May 15, 2001

Page 1466 of 1514

�FINAL REPORT
HERBICIDE (2,4-D) APPLICATOR EXPOSURE MEASUREMENTS

Harry D. Brown
106 Administration Bldg.
New Jersey Agricultural Experiment Station
Cook College, Rutgers University
New Brunswick, N.J. 08903

Supported by USDA Agreement No. USDA-TPSU-RU-0-191 and New Jersey Agricul
tural Experiment Station Project No. NJ04502.

�INTRODUCTION

The phenoxy herbicides have been used to control broad-leafed weeds in
crops, water sources, forests, pastures, range lands, gardens, lawns, urban
and industrial sites. Because of the efficiency, economy and safety, the
phenoxy herbicides, especially 2,4,5-trichlorophenoxyacetic acid (2,4,5-T)
and 2,4-dichlorophenoxyacetic acid (2,4-D), besides other herbicides, remain
essential for agricultural and other uses (Diaz-Colon and Bovey, 1976). Use
of 2,4,5-T and 2,4-D on a large scale to defoliate vegetation has resulted in
controversy about the fate of the chemicals. Many of the hazardous properties
ascribed to 2,4,5-T are to a lesser extent shared by 2,4-D. As a result, a
number of papers dealing with the fate in the environment, toxicological effects on living organisms (Diaz-Colon and Bovey, 1976; Sauerhoff et al., 1977;
Piper et al. , 1973) have been published. Cooper (1974) compared 2,4,5,-T and
2,4-D. He has reported that commercial samples of 2,4-D in mice were teratogenic and embryotoxic. Increasing controversy about their safe use has raised
doubt about their utility in achieving vegetation management objectives.
A Dow Chemical report on Forestry Applicators exposure to 2,4-D has recently been published (Levy, 1980). Nonetheless, in total, only meager information regarding human (e.g. gardeners, small farmers, etc.) exposure to 2,4-D
is available. This study reports an investigation conducted under conditions
characteristic of actual use pattern to determine the quantity of body surface
contact of applicator with the commercial 2,4-D formulation and the quantity
of the chemical measurable in serum and urine.
MATERIALS AND METHODS

Applicator
Eleven healthy young male (ages 19 to 31 years) human volunteers were selected and were examined by the University physician prior to the work. Each
subject was examined for blood pressure, pulse rate and body temperature on
the day of work, both before and after the work period, and similar examinations
were made every morning for the next three days (Table 1). Sterile gauze pads
(size 0.67 sq. ft.) were attached on the back and chest of each volunteer. A
paper cap (area 0.44 sq. ft.) was used to cover the head.
Location
The study was carried out either on the campus of Rutgers University or
near the campus in New Brunswick, New Jersey during the period from May, 1981
to August, 1981. The location was covered with weeds and grass. Each area was
roughly between one-half to one acre.
Spray Material and Equipment
The spraying material consisted of DMA-4 concentrate (obtained as a gift
from Dow Chemical, U.S.A.) which contained 3.8 Ib acid equivalent/gal 2,4-D.
The herbicide was mixed with tap water prior to use and the resulting mixture
was applied at a rate of approximately 1 gal/30 min. by a hand sprayer held at
hip level. A DuPont air sampler was attached to the applicator and was kept
running during the spraying operation. The areas were covered by spraying
six gallons in about three hours as per label instruction.

�Weather Conditions
Weather conditions during this study were moderate, temperature ranging
between 65° to 78° F with humidity from 50 to 89%. Wind was fairly calm
throughout this study except on one occasion, when it gusted to 10 miles per
hour.
Sample Collection for Analysis
• To ascertain body surface exposure, gauze pads and caps were collected
immediately after the work and washed in methanol. Air filter absorbents were
also washed in methanol. Residue separated by methanol was evaporated to dryness and then treated with 15% BF, in methanol. Finally, it was extracted
with n-hexane (Yip, 1975).
Blood samples were drawn before the work and at the end of the day's work.
Three more blood samples were drawn on the following three mornings. Overnight
pooled urine samples were collected before the work and the day's collections
were made during and/or after the treatment. Then the pooled urine samples
were collected twice a day for the next 4 to 7 days. Blood sera and urine samples were treated, extracted and analyzed by the method of Sauerhoff et al.5^
(1977).
Vegetation samples and soil samples from the treated area were collected
before the treatment and then once every 24 hours for the next 4 days after the
treatment. Samples were treated and analyzed by the methods of Davidonis et al.
(1980) and Olson et al. (1978).
Analytical Procedures
2,4-D residue extracted in n-hexane was analyzed on a pas chromatograph
(Tracer Model No. 560, equipped with electron capture detector and a six foot
glass column packed with 3% OV-101 on 80/100 supelcoport).
Clinical determinations on blood serum and urine were made through the
automated procedures of a commercial diagnostic laboratory.
RESULTS AND DISCUSSION

The various data are summarized in tables 1-13 and figures 1-22. At the
end of a day's work, an applicator had an average 2,4-D residue of 49.39 yg/sq.
ft. on the back, 52.41 yg on the head. The average value of 2,4-D residue on
vegetation in the exposed areas was 27.93 yg/g of tissue at the end of the
working day (i.e. first day). The residue fell to 8.57 yg/g tissue after four
days. On the other hand, the average soil residue value was 2.68 yg/g soil at
the end of the first working day, which Increased
to 5v12*yg/soil (87.6%)
on the fourth day.
The average base level for phenolic compounds in serum was 70.7 ng/ml at
zero level exposure. Immediately after the day's work, the value went up to
165.3 ng/ml and again went up to 267.7 ng/ml on the second. The difference
between the base level and the measured level we take to be a specific measurement of the test material, 2,4-D. The value came down to 123.7 ng/ml on the
third day. The average amount of phenolics ranged from 3.45 yg (zero level
exposure) to 7.85 yg (fifth day) for the 12 hours of pooled urine.
*Appendix A is a more extensive discussion of methodology.

�Some changes were noticed in clinical analysis made on blood aerum and
urine.
Analysis of 2,4-D retained by the air monitor filter revealed detectable
residue. The amount of air drawn through the filter was calculated to be 56.6
to 84.96 liters, and the calculated 2,4~D residue was 43.1 to 60.1 parts per
trillion.
Results of this study indicate that there was a considerable amount of
2,4-D in the air, on vegetation and soil surface of the treated areas. An
appreciable quantity of 2,4-D also landed on the body surface, All serum and
urine samples showed measurable 2,4-D residue.
Statistical Analysis *
The clinical residue and weather data were critically scrutinized by both
linear models and regression models. The primary emphasis of the analysis was
to identify the parameters that recorded any significant change. This was accomplished by subtracting the baseling value from the observed value and then
dividing it by the baseline. Analysis of the resulting values revealed highly
significant (a=0.01) changes in the serum creatinine and total protein levels,
and significant ( H . 5 change in the urine specific gravity. It was also seen
o)0)
that the total protein and BUN/creatinine were positively correlated with the
residue on the chest of the volunteers and with their height. When the peak
residue in the body fluids was related with the external factors, it was seen
that the serum residue was positively correlated with the 2,4-D concentration
in the air and the amount of chemical that had landed on the head and back.
Likewise, the urine residue was positively correlated with the air volume and
the height of the volunteers. Precipitation (rainfall-high humidity) was negatively correlated with the serum residue, presumably due to decreased chances
of vaporization and subsequent inhalation.
*Analysis done by Dr. Robert Trout, Statistician for the NJAES.
CONCLUSION
Our observations, therefore, indicate that during normal working conditions, an appreciable amount of 2,4-D can enter into the applicator's body
through inhalation and/or through body surface (dermal) absorption. Lengthy
retention times have been observed in some subjects (Table 6). These findings
are consonant with the report of Levy et al. (1980) for foresters. Clinical
physiology data obtained here are consistent with long retention times for
this chemical. We surmise, but have no specific evidence, that the 2,4-D
molecule or some portion (phenolic), binds to serum protein and is eliminated
as a function of the turnover of the protein molecules. Other than the clinical
(chemical) changes noted above, we have seen no pronounced adverse effect of
2,4-D exposure.
REFERENCES

1. Sauerhoff, M.W., Braun, W.H., Blau, G.E. and Gehring, P.J. (1977). The Fate
of 2,4-Dichlorophenoxyacetic Acid (2,4-D) Following Oral Administration to
Man. Toxicology 8:3-11.
2. Piper, W.N., Rose, J.Q., Lang, M.L. and Gehring, P.J. (1973). The Fate of
2,4,5-Trichlorophenoxyacetic Acid (2,4,5-T) Following Oral Administration
to Rats and Dogs. Toxicol. Appl. Pharmacol. 26:339-351.

�3. Levy, T.L. (1980). Determination of 2,4-D Exposure Received by Forestry
Applicators. Dow Chemical, U.S.A. Report. October, 1980.
4. Diaz-Colon, J.D. and Bovey, R.W. (1976). Selected bibliography of the
phenoxy herbicides. I. Fate in the Environment. MP 1303. Texas Agric.
Exp. Stn., College Station.
5. Cooper, P. (1974). Food Cosmet. Toxicol. 12:418-421.
6. Davidonis, G.H., Hamilton, R.H. and Mumma, R.O. ( 9 0 . Comparative Meta18)
bolism of 2,4-Dichlorophenoxyacetic Acid in Cotyledon and Leaf Callus from
Two Varieties of Soybean. Plant Physiol. 65:94-97.
7. Olson, B.A., Sneath, T.C. and Jain, N.C. ( 9 8 . Rapid Simple Procedure
17)
for the Simultaneous Gas Chromatographic Analysis of Four Chlorophenoxy
Herbicides in Water and Soil Samples. J. Agric. Fd. Chem. 26:640.
8. Yip, G. (1975). Analysis for Herbicides and Metabolites. J. Chromatographic Sciences 13:225-230.

�CLINICAL XXX DATA

�Table 1

PHYSICAL EXAMINATION

Temp ( F
°)

Blood Pressure

Pulse Rate

Applicators
0

X

1

2

3

0

X

1

2

3

0

X

1

2

3

No. 1

98.0

98.4 97.8 98.4 98.4

128/74

114/70

120/78

120/60

120/78

76

60

80

78

72

No. 2

97.6

98.0 98.0 98.0 97.8

110/78

118/78

110/78

110/72

120/80

60

72

80

68

64

No. 3

97.4

97.6 97.8 97.0 97.8

112/82

120/70

110/74

118/6?.

120/76

60

72

60

61

64

No. 4

98.2

99.4 97.4 98.0 98.0

90/60

100/68

100/64

96/68

92/60

80

100

76

76

84

No. 5

97.6

98.8 98.0 98.2 98.2

112/74

124/80

120/82

120/80

110/80

72

84

84

80

84

No. 6

97.0

98.6 97.2 97.0 97.4

120/80

110/74

108/78

112/78 112/74

84

88

96

92

100

No. 7

97.4

98.4 97.0 97.0 98.2

104/64

100/60

110/64

120/64

110/70

78

78

80

78

80

No. 8

98.4

98.4 98.6 97.8 98.0

140/76

120/80

112/70

130/68

130/76

80

64

96

80

68

No. 9

98.6

98.4 97.0 98.0 97.2

110/70

110/70

110/80

120/80

120/74

60

60

68

80

64

No. 10

97.8

98.0 97.4 98.2 97.8

104/60

100/70

108/60

112/70

102/60

84

68

84

88

88

No. 11

97.4

9 . 97.2 97.2 97.0
86

120/68

110/70

110/80

112/70

110/76

80

80

80

68

80

Legend
0 = Pretreatment
X = Posttreatment
1-3 = Days after treatment

�Table 2

Detection of 2,4-D Residue
from Gauge Patch (= Body Surface)

yg/sq. ft. 1
Applicator
No.

Head

Chest

Back

1

8.55

7.81

5.10

2

14.06

11.68

10.60

3

7.06

3.37

3.77

4

222.20

171.50

99.63

5

34.22

94.53

41.16

6

141.80

111.50

74.23

7

76.16

68.39

46.64

8

16.99

13.56

11.86

9

19.12

14.58

10.29

10

18.55

31.46

4.46

11

17.80

14.95

18.63

�Table 3
2,*i-D Residue on Vegetation

Treated
Area

2,4-D yg/g Vegetation
0

X

X+1

X+2

X+3

1

0.59

28.85

16.15

16.67

20.16

2

14.74

29.60

22. A3

4.32

2.13

3

00.00

25.35

7.70

1.92

3.44

2.47

X+4

Amount of 2,^-D on Soil Surface

Treated
Area

2,4-D -fjg/g Soil
X+1

X+2

X+3

«*

3.70

1.90

2.80

7.30

-

3.58

4.21

0.72

1.59

7.25

-

0.00

0.13

0.15

0.27

0.80

0.93

0

1

1.24

2
3

X
X
X
X

X

0
X
1
2
3
1»

=
=
=
=
=
*s

Pretreatment
Posttreatment
1 day after treatment
2 days after treatment
3 days after treatment
^ days after treatment

�Table 4
Amount of 2,4-D Residue and Endogenous Phenolic Compounds in Serum

Applicator
No.

1
2

3
k
5
6
7
8
9
10
11

0

2,4-D Residue (ng/ml )
X+1
X

75.1

826.6

114.4

170.1
131.5
112.8

112.3
54.0
93.5
157.8
56.3

221.9

208.3

123.5

44.5
3.5
29.0
19.0

224.4

00.0

00.0

443.2
538.3

19.1
50.2
7.8

496.9
862.9
119.3
55.7
41.8
93.3
55.6

X+2

311.0
250.1
74.6

92.4
169.9
94.3
194.7
43.6
43.0
58.8
27.9

X+3 .

112.3
102.3

479.6
84.2
245.1

674.6
178.6
83.4
25.7
36.3
114.8

•

0 = Pretreatment
X - Posttreatment
X+1 «= 1 day after treatment
X+2 = 2 days after treatment
X+3 = 3 days after treatment

Note: Because phenoxy and other phenolic compounds have liquid chromatographic
migrations similar to that of 2,4-D, there is a variation in the base for specific measurement of the test compound.

�\0

Table 5
Amount of 2,4-D in Serum

Applicator
No.

X

i

X+l

2,4-D (ng/rol)
X+2

714.3

198.7

0

196.1

48.3

2

60.4

116.1

3

128.4

38.0

4

285.4

5

X+3

482.0

—
440.6
654.6

6

—
—
113.6

386.1

—
188.8
466.3

7

179.9

74.8

—
150.2

8

15.6

52.2

40.1

9

21.2

12.8

14.0

10

74.3

39.8

—
17.3

11

55.6

27.9

114.8

Legend
X =
X+l
X+2
X+3

Posttreatment
= 1 day after treatment
= 2 days after treatment
= 3 days after treatment

134.1
79.9

�Table 6

Total Amount of 2,4-D and Endogenous ^henolic Comnounds Excreted in the Urine
yg 2,4-D Excreted per 12 hours

Applicator
No.

0

1

12

2k

36

48

60

1

3.73

7.12

2.38

2.58

6.49

5.70

2.93

21.20

28.96 -

-

-

-

2

3.22

7.17

1.22

2.85

6.00

5.75

4.46

6.44

-

-

-

3

2.85

4.25

10.00

8.87

1.75

0.60

1.33 10.79

1.09 4.07 -

-

-

-

4

8.11

15.44

21.38

7.66

9.56

5

0.32

1.31

1.79

1.60

1.31

6

9.95

7

9.91

8

0.00

0.11

9
10

72

84

96

108

120

132

144

156

-

-

-

-

-

-

30.55 24.87 13.09

6.23

-

-

-

-

2.62

3.32

2.27

7.39

-

-

-

-

-

I*. 56 15.62

5.04 23.39 13.87

6.28

8.46 13.16

10.81 15.25

2.73

3.12

2.89

0.91

5.00

8.84 -

-

-

-

-

0.57

2.77

1.34

3.46

2.84

3.08

5.30

1.97

1.49

2.68

0.00

0.00

0.00

0.00

0.75 0,00

0.85

2.46

8.28

6.57

1.46

4.09

1.42

2.10

3.73

2.21

4,31

4.47

0.00

1.9* 1.73

1.63

2.83

2.21

2.73

8.48

4.35 -

0 • Pretreatment
1 • Posttreatment

-

-

-

-

-

-

-

-

-

�Table 7
HEMATOLOGY

WBC x 103

liters

0

X

1

RBC x 106

RGB (g/dl)

2

3

0

X

1

2

3

HCT (%)

0

X

1

2

3

0

X

I

2

3

3. 1

6.0

7.1 6.3

7.0

5.5

4.78

j,
4.68

j,
4761

j,
4*50

j.
4.43

15.5

15.1

14.8

14.6

14.6

44.4

43.7

44.8

441.6

441.5

3. 2

5.7

6.8

5.9

5.2

5.2

4.99

5.06

5.15

4.85

4.89

15.9

15.6

16.2

15.0

15.3

43.2

43.8

44.7

42.0

42.4

3. 3

6.7

6.1

5.2

5.6

5.0

4*69

4*64

4*63

4.71

4*65

14.9

14.8

14.5

14.6

14.9

41*2

41*2

41*2

40*9

40*6

!

3. 4

6.5

7.6

6.6

6.7

6.5

5.72

5.76

5.75

5.85

5.50

15.5

15.6

15.3

16.8

14.8

43.9

44.0

43.5

44.6

41*8

!

3. 5

6.3

6.5

5.9

7.0

6.2

5.34

5.22

5.23

5.56

5.27

15.9

15.7

15.7

16.8

15.6

44.6

44.1

44.7

46.5

43.6

D.

6

6.7

7.8

6.7

8.4

6.9

5.39

5.23

5.46

5.43

5.03

16.8

16.9

17.1

17.8

16.2

47.6

46.3

48.5

47.8

44.9

3. 7

6.6

8.1

9.8

8.2

7.9

5.45

5.20

5.42

5.33

5.29

16.5

15.9

16.3

17.0

16.3

48.0

47.3

46.9

46.0

o. 8

8.3 8.3 6.2

6.3

6.1

4.97

4.75

4.99

4.99

5.04

8.1

7.8

5.21

4.76

5.07

5.42

5.14

15.8
413.2

44.1

6.0

15.7
413.9

42.6

6.2

15.7
413.2

42.8

6.1

15.2
412.4

42.9

o. 9

15.8
413.3

44.9
441.0

37*4

40*3

38.1

o. 10

7.8

7.5

8.1

7.6

7.7

4.97

5.06

5.33

5.14

16.4

17.1

16.3

4.8

6.0

6.0

5.9

4.99

4.81

4.95

5.11

14.8

14.4

14.9

14.9

45.0 43.0 45.0
4 - 4 - 4 41.2 37.8 39.3

47.1
4 40.7

45.9

5.0

15.8
•l
13*5

16.5

0.

4.80
44.54

11

Legend
0 = Pretreatment
X = Posttreatment
1-3 = Days after treatment

J.

3877

J.

35*3

X

4,

4-

42.0

J

�Table 7 (cont.)
HEMATOLOGY

MCV ( 3
y)

MCH (yyg)

MCHC (%)

Platelet Estimate

Applicators
0

X

1

2

3

No. 1

93

93

97

92

94

32J4

32^0

No. 2

87

87

87

87

87

3lt7

30.8 3lts

No. 3

88

89

89

87

87

31J8

3ll8

3ll3

No. 4

7*4

7*4

7*3

7*4

7*6

27.0

26t9

26*6

No. 5

81

81

82

81

83

29.6

No. 6

85

85

86

85

89

3l7l

32.2 31.1 32.6

No. 7

85

83

84

85

87

30.2

30.4 40.0 3lt?

No. 8

87

87

87

86

87

30.9

No. 9

7*5

7*5

7*5

7*5

7*5

24*8

No. 10

91

90

90

89

90

No. 11

83

84

83

83

83

A

0
A

X = Posttreatment
1-3 » Days after treatment

A.

2

3

A.

0

X

1

2

3

0

X

1

2

3

A.

34.7

34.3 32.9 34.9 35.1

N

N

N

N

N

31.0 31^2

36.6

35.5 36?1

N

N

N

N

N

30.8 32lO

36.0

35.9 35.1 35.4 36;6

N

N

N

N

N

28.5 27.6

35.2

35.2 34.9 37t4 35.8

N

N

N

N

N

30.0 29.7 30.1 30.3

35.4

35.5 35.0 35.8 36.2

N

N

N

N

N

35.2

36J 3

Dec N

N

N

N

31^4

34.2

35.2 34.3 35.9 35.7

N

N

N

N

3ltl

30.4 30.6 30.1

36.3

36t4

Dec N

N

N

N

25*3

25t2

33.9

34.6 34.6 33.9 34.0

N

N

N

N

N

3itg sitg site 3it2 so. 8

35.7

36.1 35.8 35.6 34.9

N

N

N

N

N

28.8

35.2

35.1 36.0 3etl 35.0

N

N

N

N

N

A

0 = Pretreatment

A,

1

32J9

A

Legend

X

A

32?0

32J3

A

A

35.6 36.0

A

A

24*9

A

A

A

33.0

24*9

28.9 29.1 29.2 28.3

•f

A

34.9 36l9

A

36^4

35.9 3ets 35.2

N

�Table 8
BLOOD CHEMISTRY

Glucose (mg/dl)

BUN (mg/dl)

Creatinine (mg/dl)

Uric Acid (mg/dl)

Applicators
0

X

1

2

3

0

X

1

2

3

No. 1

93

88

79

81

76

12

12

13

11

No. 2

78

83

63* 80

75

18

17

17

19

No. 3

93

94

92

95

87

21

21

22

No. 4

87

112+ 86

92

86

12

14

No. 5

197+ 149+ 166+ 163+ 149+ 13

No. 6

111+

No. 7

81

0

X

1

2

3

0

X

1

2

3

11

0.9

1.0

0.9

0.8

0.8

6.4

6.5

6.1

4.9

5.2

16

1.2

1.3

1.2

1.2

1.0

6.1

6.3

6.6

6.3

5.5

27+ 26+

1.0

1.0

1.0

1.1

0.9

3.8

4.5

3.9

4.8

4.1

12

13

15

1.1

1.2

1.2

1.1

1.1

7.6

7.9

7.5

8.4+ 8.1+

14

12

13

15

1.0

1.0

1.0

0.9

0.9

6.6

7.7

6.6

7.0

6.9

95

91

92

18

19

18

16

18

1.2

1.3

1.2

1.1

1.2

6.3

6.6

6.4

5.8

6.8

137+ 76

88

91

14

15

16

18

15

1.2

1.5+ 1.2

1.1

1.2

7.0

7.1

7.1

7.2

7.3

107

15

15

17

13

13

1.1

1.0

1.0

1.0

0.9

5.6

5.3

5.1

5.4

4.4

81

No. 8

122+ 102

127+ 81

No. 9

118+

90

107

79 122+

17

16

15

17

17

1.1

1.0

1.2

1.0

0.8

5.7

5.8

5.4

6.0

4.9

No. 10

101

84

134+ 99 140+

15

15

16

15

14

1.0

1.1

1.2

1.1

1.0

6.3

7.0

7.3

6.9

5.9

No. 11

148+ 124+ 112+ 98 111+

20

19

17

14

12

1.5+ 1.0

1.0

1.0

0.9

7.3

5.1

4.8

5.0

4.7

Legend
0 = Pretreatment
X = Posttreatment
1-3 = Days after treatment

�Table 8 (cont.)

BLOOD CHEMISTRY

A/G Ratio

Globulin (g/dl)

Calcium4"1" (mg/dl)

Bun/Great

Applicators

1

0

1

0

0

No. 1

2.7

2.6

2.6

2.3

2.3

1.7

1.8

1.8

1.5

2.0

13.3

12.0

14.6

14.5

14.2

4.3

4.3

4.3

4.5

4.2

No. 2

2.5

2.5

2.4

2.5

2.2

1.9

1.9

1.9

1.8

2.1

15.0

13.1

14.2

15.6

16.2

4.3

4.2

4.1

4.1

4.2

No. 3

2.4

2.4

2.3

2.4

2.2

2.1

2.0

2.2

2.0

2.2

21.0

21.0

22.0

24.5

28.5

4.4

4.5

4.5

4.3

4.5

No. 4

2.5

2.5

2.6

2.3

2.2

1.6

1.7

1.6

1.8

1.9

10.5

11.2

9.7

12.0

14.3

4.4

4.4

4.3

4.4

4.3

No. 5

3.2

3.5

3.4

3.2

2.8

1.4

1.3

1.3

1.4

1.7

12.4

13.5

12.8

13.6

16.2

3.8

3.8

3.9

4.0

4.0

No. 6

3.0

2.8

2.9

2.6

2.2

1.6

1.7

1.6

1.8

2.1

14.7

14.1

14.2

14.2

14.5

4.2

4.5

4.3

4.4

4.4

No. 7

3.1

3.1

2.9

2.7

2.5

1.6

1.4

1.5

1.6

1.8

11.7

10.1

13.6

15.7

12.7

4.2

4.2

4.3

4.4

4.3

No. 8

2.5

2.6

2.4

2.4

2.6

1.9

1.4

1.9

2.0

1.7

14.7

15.2

16.9

13.9

15.4

4.3

4.3

4.2

4.4

4.3

No. 9

2.8

2.7

2.5

2.7

2.5

1.6

1.7

1.8

1.7

1.7

15.9

15.6

12.6

17.1 "20.4

4.2

4.1

4.3

4.3

4.2

No. 10

2.8

2.7

2.8

2.5

2.6

1.6

1.8

1.8

2.0

1.8

16.0

13.3

13.4

13.3

14.1

4.2

4.2 4.2

4.4

4.2

No. 11

2.5

2.7

2.8

2.7

3.0

1.9

1.7

1.6

1.7

1.5

13.3

18.3

17.3

14.2

13.7

4.3

4.2

4.3

4.3

Legend
0 = Pretreatment
X = Posttreatment
1-3 = Days after treatment

4.1

�Table 8 (cont.)
BLOOD CHEMISTRY

Applicators

LDH (IU/1)

SCOT (IU/1) '

Alk. Phos. ( U 1
I/)

GGT (IU/1)

T. Bill, (mg/dl)

0

X

1

2

3

0

X

1

2

3

21

160

175

201

140

164

23

23

22

20

22

23

209

224

2$7

2$1

235

16

16

15

25

24

26

151

161

157

177

172

10

10

11

16

16

15

136

152

157

144

164

24

20

23

20

29

28

154

167

153

150

148

70

26

23

23

36

23

166

153

176

146

114

117

28

33

23

26

24

160

148

152

4*4

46

45

31

32

31

20

20

152

154

6*4

80

67

68

32

40

34

33

40

183

96

111

103

99

41

32

34

23

26

58

58

31

32

32

22

24

0

X

1

2

3

0

X

1

2

3

No. 1

42

40

43

45

39

22

22

20

22

No. 2

79

79

80

82

79

25

26

24

No. 3

69

61

71

79

79

22

24

No. 4

64

62

63

63

63

11

No. 5

90

81

88

87

87

No. 6

75

68

76

75

No. 7

116

111

115

No. 8

4*6

5*1

No. 9

5*2

No. 10

6*9

No. 11

116

5*8

6*1

Legend
0 = Pretreatment
X = Posttreatment
1-3 = Days after treatment

!

0

X

1

2

3

20

0.6

0.7

0.4

0.3

0.8

15

15

0.7

0.7 . . 0.7
08

0.6

11

12

12

0.4

0.6

0.5

0.7

0.4

24

24

23

21

0.5

0.5

0.7

0.6

0.4

36

36

36

39

38

0.2

0.2

0.5

0.5

0.5

145

16

15

16

14

14

0.9

0.8

1.0

its

itl

136

129

15

17

14

14

14

0.6

0.9

0.3

0.2

0.2

157

151

154

13

14

13

17

15

0.9

0.7

0.9

0.8

0.5

201

191

2$8

197

10

14

21

18

17

itl

0.8

0.9

0.7

0.9

195

179

187

169

165

16

10

11

14

12

itl

0.8

0.9

0.9

0.8

213

189

202

191

159

10

10

10

13

13

0.5

0.6

0.6

itl

1?3

�Table 8 (cont.)
BLOOD CHEMISTRY

Cholesterol (mg/dl)

T. Protein (g/dl)

Calcium (mg/dl)

Albumin (g/dl)

Applicators
0

X

1

2

3

0

X

1

2

3

0

X

No. 1

179

173

177

1(1)8

169

9.9

9.8

9.7

9.1

9.4

7.3

7.2

No. 2

223 221

215 219

175

9.8

9.6

9.3

9.5

9.3

7.2

7.2 7.0 7.2 6.7

4.7

No. 3

its

its

151

lt7

10.2

10.4 10.3 10.0 10.2

7.4

7.3 7.3

5.0 4.9 5.0 4.9 4.9

No:. 4

170 180

170 172

172

.9.6

9.7

9.4

9.7

9.2

6.7

6.8 6.7 6.6 6.4

4.1

No. 5

202 222 218 218 208

9.0

9.4

9.5

9.5

9.4

7.7

8^2 7.9

4.4 4.7

No. 6

210

208 209 208

192

10.0

9.7

7.7

7.6 7.5 7.3 6.9

4.7 4.8 4.6 4.7 4.7

No. 7

154

152

its

it?

150

10.3

9.9

9.8

9.6

stl

7.4 7.2

7.0 6.8

5to 4.4 4.3 4.3 4.4

No. 8

165

169

170

180

172

9.7

9.9

9.7 10.1

9.7

7.1

7.3

7.2 7.1

4.6

No. 9

153 160

163 163

itg

9.7

9.5

9.6

10.0

9.4

7.3

7.3 7.0 7.5 6.4

4.5 4.6 4.4 4.8 4.4

No. 10

158

168

170

168

155

9.6

10.0 10.0 10.5

9.7

7.3

7.6

7.6

7.5

7.3

4.5

No. 11

161

lt9

160

160

157

9.9

9.9

7.3

7.1

7.3 7.3

7.4

4.8 4.5 4.5 4.6 4.4

its

Legend
0 = Pretreatment
X = Posttreatment
1-3 = Days after treatment

10.6 10.2 10.1

9.6

9.5

9.9

9.9

1

2

7.1 ste

7.1

3
6.7

7.4 7.1

7.8 7.6

0

X

1

2

4.6 4.6 4.6 3t3

3
4.5

4.7 4.6 4.7 4.6

4.3 4.1 4.3 4.2
4.5 4.6 4.7

4.8 4.7 4.8 4.5

4.9 4.9 4.9

4.7

�Table 9
ACID PHOSPHATASE AND HAPTOGLOBIN

HAPTOGLOBIN (mg/dl)

ACID PHOSPHATASE (IU/1)

Applicators

0

X

1

2

3

1

2

3

4

5

No. 1

0.2 0.3

0.0

0.0

0.0

22

17

20

21

25

No. 2

0.3 0.3 0.4

0.0

0.0

24

26

24

25

18

No. 3

0.2 0.1

0.1

0.0

0.0

71

89

87

82

85

No. 4

0.0 0.0 0.0

0.0

0.04

92

113

111

76

108

No. 5

0.0 0.0 0.0

0.0

Missing

109

105

108

99

122

No. 6

0.0 0.0 0.0

0.02

0.12

189

197

204

174

238

No. 7

0.0 0.0 0.0

0.0

0.16

87

95

85

118

134

No. 8

0.2 0.0 0.0 Missing Missing

79

157

81

91

72

No. 9

0.0 0.0 0.0 Missing

0.2

90

90

91

165

80

No. 10

0.0 0.0 0.0 Missing

0.1

95

154

173

86

161

No. 11

0.0 0.0 0.0 Missing

0.6

159

114

118

118

128

Legend
0 «= Pretreatment
X = Posttreatment
1-3 «= Days after treatment

�\&lt;\
URINALYSIS

Table 10

pH

Applicators

0

X

la

Ib

2a

2b

3a

3b

No. 1

5.0

6.0

5.0

8.0

6.0

8.0

5.0

5.0 6.0

No. 2

6.0

6.0

5.0

6.0

6.0

6.0

6.0

6.0

5.0

No. 3

5.0

8.0

6.0

6.0

8.0

5.0

7.0

5.0

6.0

No. 4

5.0

5.0

5.0

5.0

6.0

5.0

7.0

5.0

6.0

No. 5

7.0

6.0

6.0

6.0

7.0

6.0

6.0

6.0

5.0

No. 6

5.0 6.0

6.0

6.0

6.0

8.0

6.0

6.0

6.0

No. 7

7.0

6.0

6.0

5.0

7.0

5.0

5.0

6.0

7.0

No. 8

6.0

6.0

6.0

5.0

5.0

6.0

6.0

7.0

5.0

7.0

5.0

8.0

No. 9

6.0

6.0

6.0

5.0

5.0

5.0

6.0

6.0

6.0

6.0

6.0

6.0

No. 10

6.0

6.0

6.0

5.0

6.0

5.0

5.0

5.0

6.0

No. 11

6.0

6.0

6.0

6.0

5.0

6.0

6.0

6.0

5.0

Legend
0 = Pretreatment
X « Posttreatment
1-7 = Days after treatment
a « 7:00 a.m. collection
b « 7:00 p.m. collection

4a

4b

5a

5b

6a

6b

7a

5.0

6.0

6.0

6.0

5.0

6.0

—

�Table 11

\ppll:ators
So. 1

Sto. 2
So. 3
No. 4
No. 5
No. 6
No. 7
No. 8
No. 9
No. 10
No. 11

0

Amber
Clear
Amber
Clear
Amber
Clear
Straw
Cloudy
Straw
Clear
Straw
Cloudy
Straw
Clear
Yellow
SI. cloudy
Yellow
Clear
Yellow
Clear
Yellow
Cloudy

URINALYSIS
COLOR

X

la

Ib

Yellow
Clear
Amber
Turbid
Yellow
Turbid
Straw
Clear
Straw
Cloudy
Straw
Cloudy
Straw
Clear
Yellow
Clear
Amber
Clear
Yellow
Clear
Yellow
Clear

Yellow
Cloudy
Amber
Turbid
Amber
Clear
Straw
Clear
Amber
Clear

Yellow
Clear
Yellow
Cloudy
Yellow
Clear
Straw
Cloudy
Straw
Cloudy
Straw
Cloudy
Straw
Clear
Straw
Hazy
Straw
Hazy
Straw
Clear
Straw
Clear

Straw
Clear
Yellow
Hazy
Yellow
Clear
Yellow
Clear
Yellow
Cloudy
Yellow
Clear

Legend
0 = Pretreatment
X = Posttreatment

2a

2b

Yellow Yellow
Clear
Clear
Yellow Yellow
Cloudy Cloudy
Yellow Yellow
Clear
Clear
Straw Yellow
Clear
Cloudy
Yellow Yellow
Cloudy
Hazy
Straw Yellow
Cloudy
Hazy
Straw Yellow
Clear
Clear
Straw Yellow
Cloudy
Hazy
Straw Yellow
Cloudy
Hazy
Straw
Straw
Clear
Clear
Straw
Yellow
Clear
Clear

1-7 = Days after treatment
a = 7:00 a.m. collection

3a

3b

Yellow
Clear
Yellow
Clear
Yellow
Clear
Yellow
Clear
Yellow
Clear
Yellow
Cloudy
Yellow
Clear
Yellow
Clear
Yellow
Clear
Yellow
Clear
Yellow
Clear

Yellow
Clear
Yellow
Turbid
Yellow
Clear
Yellow
Cloudy
Yellow
Cloudy
Yellow
Cloudy
Yellow
Cloudy
Yellow
Clear
Yellow
Cloudy
Yellow
Clear
Yellow
Clear

4a

4b

5a

5b

6a

. 6b

7a

Yellow
i
Clear
Yellow
;—
Turbid
Yellow
—_
Turbid
Yellow
—;_•
Cloudy
Yellow
Cl Dudy
Yellow
Cloudy
Yellow
Cloudy
Yellow Yellow Yellow Yellow Yellow Yellow Yello
Clear
Hazy
Cloudy Hazy
Clear
Clear
Hazy
Yellow Yellow Yellow Yellow Yellow Yellow Yello
Clear
Clear
Clear
Clear Clear
Clear
Hazy
Yellow
Clear
Yellow
Turbid

7:00 p.m. collection

�Table 12
URINALYSIS
SPECIFIC GRAVITY

Applicators

4a

4b

5a

5b

X

la

Ib

2a

2b

No. 1

1.022

1.010

1.026

1.007

1.015

1.010

1.023

1.010

1.015

1.028

1.027

1.028

1.028

1.024

1.024

1.026

1.033

1.028

1.033

1.023

1.030

1.026

1.033

1.020

1.024

1.015

1.022

1.008

1.020

1.020

1.020

1.018

1.024

1.019

1.022

1.018

1.020

1.022

1.022

1. 016

No. 6

1.029

1.028

1.025

1.024

1.026

1.017

1.029

1.024

1.012

1.014

1.016

1.016

1.017

1.014

1.020

1.014

1.026

1.026

1.020

1.022

1.026

1.027

1.027

1.012

1. 015

1.017

1.023

1.024

No. 9

1.013

1.027

1.025

1.025

1.031

1.031

1.030

1.032

1. 015

1.030

1.025

1.020

No. 10

1.017

1.018

1.026

1.007

1.008

1.006

1.021

1.011

1. 018

No. 11

1.025

1.016

1.017

1.020

1.022

1.012

1.016

1.012

1. 025

1.026

1.015

1.023

1.023

1. 012

No. 8

1.026

1. 028

'No. 7

1.030

1. 016

No. 5

_—

1. 030

No. 4

7a

1. 029

No. 3

6a

1. 006

No. 2

6b
— _.

0

Legend
0 = Pretreatment
X = Posttreatment
1-7 = Days after treatment
a = 7:00 a.m. collection
b = 7:00 p.m. collection

3a

3b

.
—

�Table 13

U « I * AL » I I S

Appllcatort

0

1

l a

II

BACTERIA
?ew
CRYSTALS
Calcium
Oxalete

tPITH-.
Occet.
CRYSTALS
vValet

I t

la

CRYSTALS IPITHi
Uric
Rare
acid.
Urates

Jb

3a

CPITH:

fPtTH'

wnc-0-l

1-1

b-r

Jo

tfitiji.

Occet.
IPIIH:
CRYSTALS Occas.

k-» Cal-

It

BACTERIA BACTERIA CRYSTALS CPITNi
CRYSTALS XBCiO-l WBC
Few
Few
Calcium Few
Urates
IVTTHi
Rare
. Oxalate CRYSTALS
TI ' CPITHj
Urates
CRYSTALS TT"^
8-1 Cal- CRYSTALS
clue
0-1 Calctum
OxaUta

1
1

BACTERIA BACTERIA UBC:J-J
Few
Few
rRYS~TAL$
CRYSTALS PROTEIN:
clum
Calcium ~\
Oulata
Oxalata

PROTEIN; (PITHs

UBC:0-I

Few

RaTe

Ful 1

0-1

VBC; 0-1 UBC:0-I

£r*-

WBC: 0-1

WBC:0-t
tpTTHi

V3C:0-I W)C:l-2
laVTTALS IFfTH:

VBC:0-2
trTTrli

WBC:0-1
BTTH:

Few ~*

Few

?S

few

CRYSTALS Celclio

Few

11

IJ

Oxalates.
many
amor-

It

EPITH,
WSC:0-I
few—
CTiYTTALS
CRYSTALS Hi&gt;|c
CRYSTALS CRYSTALS CRYSTALS Calcium acid.
Calcium AmorFew Cal- OxaCalcium
Ouclum
phous
late,
Oxalate
late.
•rates
Oxalate, Uretas
CLUCOSE
Few
CLUCOSE •wny
Trace
amorTrace
phous

0-1

WBC:0-I tf»C:0-l
UBC:0-I UBC:0-t
CRYSTALS EPITH:
CTiV5TAts
Calcium
Few cat - few
Oxalase, CRYSTALS Clum
AmorCalcium Oxalate
phous
Oxa late- CASTS:
0-fc
urates Few.
byline
Amorphous
casts
•rates

tPITH;
Occas.
CRYSTALS
CRYSTALS Phos•
Few cel- phetes
clum
BLOOO:
Oxalate. TI
Few
mucus
threads
WDC:0-I
EPITH:

Few

UBCiO-t WBC:0-I UBC:0-I ViCiO-l UDC:0-t WBC:0-I
tpTTH:
IfTTH:
IFTTB:
Few
Few
FI
BACTERIA
Few
CRYSTALS
Urates
tPTTn:

msa

in—

w«C:0-t
tTTTH: IF7TH:
Rare
CRYSTALS CRYSTALS
Occas. liare
Calcium Calcium
Oxalate
2* Amorphous
Urates.
2» Hucus

VtC:l-l

n w«c!o-i
l^rt

W!C:0-I
t?ll«:
Rare
YSTALS
re
Calcium
Oxalate,

tPITHl
.
Occas.
CRYSTALS

WBC:0-I
|ljre '

W8C:0-I
IPlTH;
Rare

EPITH:
CRYSTALS - .
Occas.
CRYSTALS
Urates

{PITH: WBC-.I-J CRYSTALS .
Occas .
CRYSTALS Urates acid.
Urates
Urates

nvTTALs urn

CRYSTALS WBC:I-J
tfTTHs
phOUS
Occas.
SediCRYSTALS
ments
Urates
JLOOD-.I*

*zr-—

WBC:0-I CRYSTALS CRYSTALS EPITH:
Calcium Occas.
Full
Oxalate BACTERIA
Field
itoJ:
Amor•mount,
phous
SediFew
ment
mucus
threads

CRYSTALS - '

.

.

.

.

.

.

.

.

.

.

.

.

.

.

.

.

.

.

.

.

.

.

RBC:Rara
ITtTH:
Occas.
Few
awicus
threads

rcq&lt;

threads
yjCup-l JSCj.O-1
tflTH:
CPITHi
Rare
Rare
BACTERIA.
Full
field

MliOO
tPITHL
Rare

W1C;0-I

VlCiO-t
ITTTH;
Rare

iTTfHi

m

phous
Urates

MICWft

VtC:0-l VBCJM
I?TlHj. PTfrl:
lire
Rare
BACTERIA
:TERIA

.

Im-

S

V»C:0-1

CRYSTAL!I
f requenlt
Calcium
Oxalate,i
I* IhlCUS 1* rtocuiI
Threads Threads

fit

.

BACTERIA WK:0-t IACTERIA PROTEIN BACTERIA V&gt;C:0-I
1+
Hoderate P.BC:Rare
Many
TRYTTAIS Many
HlYS~TALS
CRYSTALS Calciun CRYSTALS BACTERIA
Few
•
Celclum
Calcium Oulate AmorCRYSTALS
Oxalate.
phous
Oxalate
Amor1* Mucus
Phosthreads .
phates phous
Urates,
Calcium
Oxalate

CRYSTALS YSTALS tPITH: CPITH^ tPITH; CRYSTALS tPITH: tPITH;
OccaOcca- ' Moderate Calcium ! T
P
Calcium
Iclim Few
Oulate CRYSTALS slonal
Oxalate, Oxalate BACTtRIA slonal
Calcium
CASTS; AmorOxalate
Calcium phous
Field
CRYSTALS
Oxalate Sediment
Moderate
PROTEIN;
«t
amount
Calcium
Oxalate.
Few

wfit1 f
frequent

S

IPITH:
CfltH:
Rare
Rare
fRYSTALlHYSTAlS
frequent Rare
Calcium Calcium
Oxalate Oxalate

-

t.|

phous
•rates

amorphous

7a

Occat.

BACTERIA UBCil-J
W»C:»-1 .
ITTTH;
Occas.
CRYSTALS ilralts
CRYSTALS Few
BLOOD I* Urates
Urates
CRYSTALS
PROTEIN
Orates

ITTTH:

JP1

CRYSTALS r^

field
amorphous
•rates

K

»b

«o»

•

VBC:0-I WBClO-l
CTlTTALS

(a

amorewcus •
threads. phous
sperurates
ewto-

CRYSTALS CRYSTALS
Urates &gt;hos-

Ik

Sb

WIT

EPITH;
CftWAlS •
Occas.
Lg. «Mt.
CRYSTALS I
CJTV
amorphous
few uric
«rates, &lt;
few calcium
mulata

tPTTH;
Occas.

vn*

mucus- .
threads

ten

ia

&lt;*-

VBC

'o-i

+1
WBC: 1-2
Occas.
BACTERIA IFfTHl

&lt;*

VBC-

clum
Oulata

i

Ve

VBCiO-l
tMTH!
Rare

tPITH;
tPITH;
Rare
Rare
BACTtRIA
Faw

-

tPITM:
Rare

UO&amp;i.
Bcce llonal

tPITH:

tPITH;
Occa-

CRYSTALS
Calcium

slonal

Oxalate

�Figure 1. 2,4-D and Endogenous Phenolic Compounds Measured in Serum

1.0

_

0.6

_

0.4

0
X
1
2
3

,-

0.8

Subject No. 1

_

&lt;u
CO

C£

0.2 .

Day

= Pretreatment
• Posttreatment
= 1 day after treatment
= 2 days after treatment
= 3 days after treatment

�Figure 2.

2,4-D and Endogenous Phenolic Compounds Measured in Serum

0
X
1
2
3

1.0

0.8

M
&lt;U

Subject No. 2

0.6

cn
Q

0.4
00

0.2

\_
1
Day

«
»
=
=
=

Pretreatment
Posttreatment
1 day after treatment
2 days after treatment
3 days after treatment

�Figure 3.

1.0

2,4-D and Endogenous Phenolic Compounds Measured in Serum

Subject No. 3
0
X
1
2
3

i-

0.8

0)
CO

0.4
60

0.2

1
Day

= Pretreatment
= Posttreatment
= 1 day after treatment
= 2 days after treatment
= 3 days after treatment

�Figure 4. 2,4-D and Endogenous Phenoli: Compounds Measured In Serum

1.0

r.

0.8

0.6
CO

a

0.4
00

0.2

I
1
Day

Subject No. 4
0 = Pretreatment
X « Posttreatment
1 = 1 day after treatment
2 = 2 days after treatment
3 = 3 days after treatment

�Figure 5. 2,4-D rahd Endogenous Phenolic Compounds Measured in Serum

1.0 _

0.8

0.6

0.4

0.2

1
Day

Subject No. 5
0 = Pretreatment
X = Posttreatment
1 = 1 day after treatment
2 = 2 days after treatment
3 = 3 days after treatment

�Figure 6.

0.8

0.6

p
0.4

0.2

Subject No. 6
0
X
1
2
3

1.0

&lt;u

2,4-D and Endogenous Phenolic Compounds Measured in Serum

-

=
=
=
=
=

Pretreatment
Posttreatment
1 day after treatment
2 days after treatment
3 days after treatment

�Figure 7.

2,4-D and Endogenous Phenolic Compounds Measured in Serum

0 = Pretreatment
X = Posttreatment
1 « a day after treatment
2 * 2 days after treatment
3 = 3 days after treatment

1.0

0.8

to 0.6
en
H
0

00

Subject No. 7

0.4

3.

0.2

1
Day

�Figure 8. 2,4-D and Endogenous Phenolic Compounds Measured in Serum

1.0

0.8

0.6
&lt;u
en

0.4
OC

0.2

1
Day

Subject No. 8
0 » Pretreatment
X = Posttreatment
1 = 1 day after treatment
2 = 2 days after treatment
3 = 3 days after treatment

�Figure 9.

2,4-D and Endogenous Phenolic Compounds Measured in Serum

0 « Pretreatment
X = Posttreatment
1 = 1 day after treatment
2 = 2 days after treatment
3 = 3 days after treatment

1.0

0.8

g
to

Subject No. 9

0.6

0.2

1
Day

�Figure 10.

1.0

0.8

S&gt;

0.6

CO

o
sf
«M

tn

0.4

0.2

2,4-D and Endogenous Phenolic Compounds Measured in Serum

Subject No. 10
0
X
1
2
3

» Pretreatment
» Posttreatment
= 1 day after treatment
= 2 days after treatment
= 3 days after treatment

�Figure 11. 2,4-D and Endogenous Phenolic Compounds Measured in Serum

1.0

0.8

$ 0.6

V)

C5
CM

be

04
.

0.2

Subject No

0
X
1
2
3

11

Pretreattnent
Posttreatment
1 day after treatment
2 days after treatment
3 days after treatment

�Applicator No. 1
0 » Pretreatment
X « Posttreatment

Figure 12. Amount of Total 2,4-D and Endogenous Phenolic Compounds
Excreted in Urine
30

20

12

24

36

48

60
Hour

72

84

96

108

120

132

144

�30

Figure 13. Amount of Total 2,4-D and Endogenous Phenolic Compounds
Excreted in Urine

Applicator No. 2
0 «• Pretreatment
X = Posttreatment

20

o
•ato
* 10

12

24

36

48

60
Hour

72

84

96

108

120

132

144

�30

Figure 14. Amount of Total 2,4-D and Endogenous Phenolic Compounds
Excreted in Urine

20

p
L

10

Hour

Applicator No. 3
0 - Pretreatment
X = Posttreatment

�Figure 15. Amount of Total 2,4-D and Endogenous Phenolic Compounds
Excreted in Urine

Applicator No. 4
0 = Pretreatment
X = Posttreatment

30

20 .

cd

4J

o
CM

t&gt;0

10

12

24

36

48

60
Hour

72

84

96

108

120

132

144

�30

Figure 16. Amount of Total 2,4-D and Endogenous Phenolic Compounds
Excreted in Urine

Applicator No. 5
0 - Pretreatment
X = Posttreatment

20

JC

10

120

Hour

132

144

�Figure 17. Amount of Total 2,4-D and Endogenous Phenolic Compounds
Excreted in Urine

12

24

36

48

72

60

Hour

84

Applicator No. 6
0 Pretreatment
X Posttreatment

96

108

120

132

144

�30

Figure 18. Amount of Total 2,4-D and Endogenous Phenolic Compounds
Excreted in Urine

Applicator No. 7
0 = Pretreatment
X = Posttreatment

20

o

H

CM
00

X

12

24

36

48

60
Hour

72

84

96

108

120

132

i
144

�30

Figure 19. Amount of Total 2,4-D and Endogenous Phenolic Compounds
Excreted in Urine

20

rt
jj
o

6C

10

Hour

Applicator No. 8
0 * Pretreatment
X = Posttreatment

�30r

Figure 20. Amount of Total 2,4-B and Endogenous Phenolic Compounds
Excreted in Urine

Applicator No. 9
0 * Pretreatment
X » Posttreatment

20-

«8
•U

Q
CM

00

10-

X

12

24

36

48

60

72

Hour

84

96

108

120

132

144

�30 r

Figure 21. Amount of Total 2,4-D and Endogenous Phenolic Compounds
Excreted in Urine

Applicator No. 10
0 = Pretreatment
X - Posttreatment

20

O

H

(50

3-

10

I

12

24

36

48

60

72

Hour

84

96

108

120

132

144

�30 r

Applicator No. 11
0 » Pretreatment
X = Posttreatment

Figure 22. Amount of Total 2,4-D and Endogenous Phenolic Compounds
Excreted in Urine

20

10

12

24

36

48

60

72

Hour

84

96

108

120

132

144

�MS*
Appendix

Methodology for 2,4-D Analysis

�Methods for Analysis of 2,4-D
In order to select the most recent analytic techniques for 2,4-D assay
in urine, serum, gauze patches, vegetation and soil samples, a literature
survey was done. The following methods were used in our investigation:
a. Urine: Out of the total volume of urine samples, 10 ml was taken and
2 ml of IN HC1 was added to it. The acidified urine was then mixed with 5 ml
of diethyl ether and was shaken for 10 minutes on a Buchler-Vortex -evaporator
(Vortex setting was kept at 5). This extraction method was followed three
times. The ether extracts were pooled together and evaporated to complete
dryness at a temperature not higher than 45°C. The dry residue was dissolved
in 1 ml of methanol first and then mixed thoroughly with 1 ml of 15% solution
of BF3 in methanol. The resultant mixture was heated in a water bath at 70°C
for 10 minutes for complete methylation. The methylated solution was cooled
and again extracted thrice with 1 ml of n-hexane. N-hexane extracts were either
injected (1 yl) immediately in a G.C. or stored at -20°C.
b. Blood Serum: One ml of isolated serum was diluted with 4 ml of distilled
water and then acidified with 1 ml of IN HC1. The acidified serum was then
treated (i.e. extracted and methylated) in exactly the same manner as was the
urine. One yl of n-hexane extract was injected in a G.C.
c. Gauze Patches: Immediately after the day's work, the patches (from the
front, back and head cover) were soaked separately in 100 ml of methanol and
kept overnight at 4°C. After washing the patches thoroughly with methanol, 50
ml of the wash (from each group) was evaporated to dryness at less than 45°C
temperature. The dry residue was dissolved in 1 ml of methanol and then methylated and finally extracted as above. The methylated compound, however, was
attracted three times with 4 ml, 3 ml and finally 3 ml of n-hexane. The pooled
extractant was diluted when needed before G.C. analysis or stored as before at
-20°C.
d. Air Filter: Each air filter was washed with 50 ml of methanol immediately after the day's work and was kept at 5°C overnight. Clear methanol was
removed and the filter was further rinsed twice with 10 ml of methanol. The
pooled methanol was treated in the same way as the gauze patches.
e. Vegetation: Ten grams of freshly collected leaves were chopped and homogenized in 50 ml of 95% hot ethanol. The homogenate was centrifuged at 5,000
rpm in a fixed angle rotar for 30 minutes. Supernatant was carefully removed
and saved. The pellet was thoroughly washed with 50 ml of 80% hot ethanol and
recentrifuged three times as before. Each supernatant fraction was pooled together in a round bottom flask and was evaporated to bring the final volume to
20 ml. The concentrated supernatant was adjusted to pH 3 by adding exactly
10 drops of H3PO^. This acidified solution was extracted first with 50 ml of
diethyl ether and then with 25 ml and finally with 25 ml of diethyl ether. The
total extractant was evaporated to dryness under a current of nitrogen at 45°C.
The dry residue was again extracted three times with 3ml, 1 ml and 1 ml of
methanol. The combined methanol extract was treated with 1 ml of 15% BF2 in
methanol and kept under a nitrogen atmosphere in a water bath at 70°C until
concentrated to 2 ml. This methylated solution was further extracted with nhexane as described above. N-hexane was diluted when needed for G.C. analysis.

�f. Soil: Fifty prams of soil sample was mixed with 40 ml of IN H^SO, to
prepare a slurr. To the acidified soil, 45 ml of diethyl ether was added and
was taken in a separating funnel for extraction. The separating funnel containing the soil sample was shaken for a total of fifteen minutes, but for not
more than one minute at a time. The solvent layer was decanted and passed
through glass wool and the aqueous layer containing soil particles was rejected.
The clear solvent layer was then mixed with 25 ml of IN NaOH and shaken vigorously in a separating funnel for 1 minute. The organic layer was rejected and
the alkaline aqueous layer was cleaned by partition method with 25.ml chloroform. The clean aqueous layer was further acidified with 1 ml of cone. l^SO^
and extracted with 25 ml of ether. The ether extract was dried completely and
redissolved in 5 ml of methanol. Methylation and final n-hexane extraction
were made as in the case of the vegetation samples.
The following gas chromatographic conditions were used:
Detector, Electron capture Ni 63 temperature: 350°C
Gas: Methane: Argon
(5:95)
Flow rate through the column
25 ml/min
Sample volume injected
1 yl
Column material
3% 0V 101 on 80/100 supelcoport
Length of the column
6 ft
I.D. of the column
2 mm
Column temperature
187°C
Injection port temperature
200°C

�</text>
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&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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                <text>1974</text>
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            <description>A name given to the resource</description>
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                <text>Absorption and Excretion of 2,4,5-Trichlorophenoxy Acetic Acid in Man</text>
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            <name>Subject</name>
            <description>The topic of the resource</description>
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                <text>human testing</text>
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              <name>Title</name>
              <description>A name given to the resource</description>
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                  <text>Alvin L. Young Collection on Agent Orange</text>
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                  <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>Series III Subseries I</text>
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            <name>Creator</name>
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                <text>Kolmodin-Hedman, Birgitta</text>
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            <name>Source</name>
            <description>A related resource from which the described resource is derived</description>
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                <text>Arhiv za higijenu rada I toksikologiju</text>
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            <name>Date</name>
            <description>A point or period of time associated with an event in the lifecycle of the resource</description>
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                <text>1973</text>
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            <name>Title</name>
            <description>A name given to the resource</description>
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                <text>Changes in Drug Metabolism and Lipoproteins in Workers Occupationally Exposed to DDT and Lindane</text>
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            <name>Subject</name>
            <description>The topic of the resource</description>
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                <text>human testing</text>
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