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                    <text>Rom D Number

02239

Author

Tumasonis, Casimir

Corporate Author
Report/Article Title Typescript: Preliminary Report: Chick Embryos as a
Probe of the Relative Toxicities of Soot Samples from a
Polychlorinated Biphenyl-Containing Transformer, [nd]

Journal/Book Title
Year

Month/Day
Color
Number of unaoes

n

14

Descriptor) Notes

Thursday, September 20,2001

Page 2289 of 2293

�PRELIMINARY REPORT
CHICK EMBRYOS AS A PROBE OF THE RELATIVE
TOXICITIES OF SOOT SAMPLES FROM A POLYCHLORINATED
BIPHENYL-CONTAINING TRANSFORMER

Casimir Tumasonis and Laurence Kaminsky

Division of Laboratories and Research
New York State Department of Health
Albany, New York 12201

�Chick Embryos as a Probe of the Relative Toxicities of Soot Samples
from a Polychlorinated Biphenyl-Containing Transformer.

Tumasonis, C.

and Kaminsky, L.
The involvement of a polychlorinated biphenyl (PCB)-containing
transformer in a fire resulted in widespread contamination of the
State Office Building in Binghamton, New York with a soot-like
material containing 1 ppm 2,3,7,8-tetrachlorodibenzo-p-dioxin
(2,3,7,8-TCDD), 50 ppm 2,3,7,8-tetrachlorodibenzofuran (2,3,7,8-TCDF),
and relatively high concentrations of PCBs and other polychlorinated
dibenzofurans and dibenzodioxins.

The chick embryo system has been

investigated as a rapid and inexpensive method for assessing the
relative toxicities of large numbers of soot samples derived from
different sites in the building, and as a means of assessing
effectiveness of the clean up procedures.

Samples were administered

to the embryos in an aqueous 0.75% methyl cellulose vehicle via a hole
drilled into the shell over the air sac.

Soot exhibited the greatest

embryo lethality when administered on day 4 of incubation.

There was

a non-linear dose related embryo lethal response with a marked saturation of embryo lethality between the 0.2 and 2.0 mg soot/egg doses.
At 2.0 mg soot/egg administered in 0.1 ml aqueous vehicle approximately 50% of the embryos were dead by day 18 of incubation.

No

deaths were observed with the same quantities of active carbon or
fireplace soot.

Increasing volumes of vehicle increased the embryo

lethal effects of the soot probably indicating that the non-linear
dose response was partially due to a lack of availability of all the
administered soot to the' inner air sac membrane. At doses of 2.0 mg
Binghamton soot/egg some teratological effects were observed in

�embryos surviving to day 18 of incubation. The effects included
curled toes, anophthalmia, exencephaly and edema and occurred at low
frequency and non-reproducibly.

2,3,7,8~TCDD when administered into

the eggs at doses of up to 500 ng/egg in the aqueous vehicle and up to
800 ng/egg in corn oil killed 3 out 15 embryos at the highest dose and
all embryos above 10 ng/egg in the two vehicles respectively.

Further

studies are underway to develop the chick embryo system for use in
investigating the relative toxicities of different soot samples.

�A fire which involved a transformer in the State Office Building
in Binghamton, New York resulted in extensive contamination of the
building with a soot-like material.

The transformer contained a

dielectric fluid (pyranol) which comprised 65% Arochlor 1254 (a polychlorinated biphenyl (PCB) mixture), 35% chlorinated benzenes and
trace

additives.
Soot samples collected from two sites in the building were •

contaminated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (2,3,7,8-TCDD)
and 2,3,7,8-tetrachlorodibenzofuran (2,3,7,8-TCDF)(Smith et al.,
1981a).

Based on pyrolysis studies with PCBs it was predicted that

the soot would also have relatively large contamination by other
isomers and congeners of the polychlorinated dibenzo dioxins and dibenzofurans (Buser _et al., 1978).
Predictions of the toxicity of the soot based on the known
concentrations and toxicities of 2,3,7,8-TCDD and 2,3,7,8-TCDF are
suspect for a number of reasons:

Not all contaminating components of

the soot can be determined, the toxicities of all polychlorinated
dibenzodioxins and dibenzofurans is not known, the role of the soot
matrix was not known (Silkworth et al., 1981) and the potential for
synergistic or antagonistic effects of the pollutants on the toxicity
of other pollutants is unknown.

Thus there was a requirement for a

toxicological assessment of the soot where it would be treated as a
single compound.
As part of the clean-up procedures in the building, assessments
of the variations in toxicity of soot from different sites and at
different times as the clean-up proceeds will require toxicologic
analysis of numerous samples.

A method was required which would

provide a rapid analysis of large numbers of samples without enormous

�resources of personnel and equipment.
using chick embryos.

These criteria could be met by

In 1966 a group meeting under the auspices of

the World Health Organization recommended that the chick embryo not be
used for screening drugs for teratogenicity since it is "too sensitive
to a wide range of agents and affords no parallel with the anatomical
and physiological relationship existing between a pregnant mammal and
her conceptus" (World Health Organization, 1967).

Subsequently argu-

ments have been raised in favor of the introduction of the use of
chick embryos in teratology most notably by Gebhardt (1972) in the
Netherlands and Wilson (1978) in the USA.

A number of reports have

appeared recently in which the chick embryo method has been used to
investigate the teratogenicity of methylene chloride, trichlorethane,
trichloroethylene, tetrachloroethylene and toluene (Elovaara et al.
1979), DDT (Swartz, 1980), cholinergic insecticides (Misawa et al.,
1981) and Lambda-Carrageenan (Monis and Ravasio, 1981).

The chick

embryo has also recently been used to evaluate the cardiovascular
teratogenicity of 2,3,7,8-TCDD (Cheung et jal., 1981).
In this paper we report our preliminary investigations on the use
of the chick embryo to investigate the relative toxicities of samples
of soot collected in the state office building.

The main criterion

which will be used is embryo lethality rather than teratogenicity in
view of the controversy associated with interpretation of teratological effects and the relative ease in assessing embryo lethality.

�METHODS
Fertile White-Leghorn chicken eggs (50-60 g) were obtained from
a farm maintained by this Division.

After collection the eggs were

placed into a humidified (65-67% humidity), forced-draft incubator
(Humidaire) and were incubated at 37.5° ±0.32°C to initiate embryo
development.
Contaminated soot was obtained with a vacuum cleaner fitted with
clean collection bags from the stairwells of the third and fourth
floors of the State Office Building in Binghamton, New York.

It was

filtered through a wire gauze to remove gross inert contamination.
Extracts of the soot were prepared by Soxhlet extraction with benzene
for 16 hr.

Benzene was removed by heating the solution.

2,3,7,8-TCDD

was obtained from Dow, Midland, MI as a solution in toluene.

The soot

was analyzed as previously reported (Smith _et al., 1981b).
For administration of samples a small hole was drilled into the
egg shell in the center of the airspace (determined by candling) and
samples injected by a syringe (fitted with an 18g needle) onto the
inner membrane.

The hole was then immediately sealed with paraffin

and the eggs incubated.

At the end of the incubation period eggs were

cracked open and the embryos were removed and evaluated for lethality,
gross malformation, and subcutaneous edema.

Surviving and non-auto-

lized embryos were individually preserved in 10% neutral buffered
formalin.
Studies were performed to determine the optimal day of administration and day of termination, dose response-curve, effect of volume
of vehicle, effect of polarity of vehicle and effect of the soot
matrix on the toxicity of contaminants.

The last study will be per-

formed by comparing the embryo lethality of the soot itself with that

�of the benzene extract of the soot.

Effect of vehicle polarity was

tested using 2,3,7,8-TCDD as the test compound.

The vehicle chosen

for most of the studies is 0.75% aqueous methyl cellulose.

A similar

system has recently been demonstrated to be a safe vehicle in teratological studies (Fritz and Decker, 1981).

This vehicle has also been

used in extensive studies of the toxicity of the soot in guinea pigs
(Silkworth et al., 1981).

�RESULTS AND DISCUSSION
Thirty eggs were randomized into three groups of 10 each.

On

each of days 0, 3 or 4 of incubation one of the groups was inoculated
with 2.0 mg spot/egg in 0.75% aqueous methyl cellulose (0.1 ml/egg).
One half of each group was opened on day 14 and the remainder on day
18, and the embryos examined for viability.

Administration on days 0,

3 and 4 resulted in a total of 17, 38 and 78% embryo deaths respectively.

It was thus apparent that administration on day 4 was the

most effective for the expression of soot toxicity in this system and
all subsequent studies incorporate administration on day 4.
In a series of studies designed to determine the dose response
and reproducibility of embryo lethality, eggs were administered 0.02,
0.2 or 2.0 mg soot/egg in aqueous methyl cellulose into the air sac on
day 4 of incubation.

In each study 15 eggs/group were used.

Two

control articles, fireplace soot and active carbon, were also inoculated separately on day 4 into the air sac at doses of 2 mg/egg in the
aqueous vehicle.
lethality.

In no case did the control articles result in embryo

In two separate experiments 2 mg soot/egg led to 53 and

56% dead embryos indicative of the reproducibility of the system.
However, studies repeated at periods over several months showed much
greater variability.

In one of these experiments only one of the

soot-exposed embryo which survived the 18-day incubation exhibited
anophthalmia, exencephaly, toe curl and a short upper beak while four
other embryos exhibited edema.

Toe curl was found for the majority of

the chicks surviving up to the 18th day.

In the duplicate experiment

the only gross teratological effect observed was toe curl.
In Fig. 1 the dose response curve for embryo lethality is shown.
There was a marked saturation in embryo lethality between the 0.2

8

�mg/egg and 2.0 rag/egg close levels.

To explain this we hypothesized

that the aqueous soot-containing vehicle would form droplets on the
inner membrane and that some' of the soot, distant from the droplet
surface exposed to the membrane, would not be available for xenobiotic
release to the embryo.

To test this hypothesis we administered to

groups of 15 eggs, doses of soot in differing volumes of vehicle.
Doses of 1 mg/egg and 0.1 mg/egg were administered in 0.05, 0.10, 0.50
and 1.00 ml aqueous vehicle.

No volume effect was noted at the low

dose but at the high dose lethality increased with increasing volume
until the highest volume where embryo lethality was diminished.

Mor-

talities were 13% at 0.05 ml, 20% at 0.1 ml, 40% at 0.50 ml and 27% at
1.00 ml.

It is thus possible that low vehicle volume prevents com-

plete exposure of the soot to the membrane.
In a recent study (Cheung et al.f 1981) 2,3,7,8-TCDD was administered into the egg white of fertile chicken eggs in a vehicle of acetone/corn oil at doses of 0.003 to 25 ng/egg on day 0 of incubation.
At no dose was there more than 45% lethality.

The soot sample used in

the current study has been reported to contain approximately 1 ppm of
2,3,7,8-TCDD and 50 ppm 2,3,7,8-TCDF (Smith et al., 1981b).

At a dose

of 2 mg soot/egg there was thus approximately 2 ng 2,3,7,8-TCDD/egg
and 100 ng 2,3 ,7 ,8-TCDF/egg.
In an effort to compare the soot embryo lethality with that of
one of its similarly administered components, and to determine the
effect of the aqueous vehicle relative to a more hydrophobic vehicle
2,3,7,8-TCDD was administered to the eggs in aqueous methyl cellulose
or corn oil vehicles.

Groups of 15 eggs received 0.1, 1.0, 5.0, 10.0,

100, 250 or 500 ng TCDD/egg in 0.1 ml aqueous methyl cellulose, or 10,

�50, 100, 250 or 800 ng TCDD/egg in 0.10 ml corn oil, or 0.1 ml of the
vehicles on day 4 of incubation, into the air sac.

With the aqueous

vehicle only the two highest doses were embryo lethal producing 1 and
3 deaths respectively.

In contrast all doses above 10 ng/egg in corn

oil killed all the embryos.

The corn oil vehicle killed 4 embryos.

While this study has not been completed it is apparent that the embryo
lethality of the soot probably does not arise from the bound 2,3,7,8TCDD.
The effect of corn oil itself in killing 27% of the embryos is
consistent with a previous report that olive oil (25 yI/egg) injected
into the air sac on day 3 of incubation killed 27% of the embryos by
day 14 of incubation (Elovaara et al./ 1979).

However, in another

study (Kitos et al., 1981), corn oil when injected into the yolks of
eggs at 50 yl/egg on day 6 of incubation produced no deaths of embryos
by day 18.

In conclusion we have demonstrated that the Binghamton soot
produces embryo lethal effects when administered into the air sacs of
fertile eggs under conditions where active carbon and fireplace soot
have no effect.

The lethal effects are dose dependent and also

dependent on the volume of administration vehicle.

One of the

components of the soot, 2,3,7,8-TCDD, is markedly more toxic when
administered in corn oil-than in an aqueous vehicle and it is possible
that the apparent toxicity of the soot is similarly dependent on
vehicle polarity.

Further studies are underway to develop the chick

embryo method for evaluation of relative toxicities of Binghamton soot
samples.

10

�REFERENCES
BUSER, H. R., BOSSHART, H.-P., and RAPPE, C. (1978).

Formation

of polychlorinated dibenzofurans from the pyrolysis of PCBs.
Chemosphere 7, 109.
CHEUNG, M. 0., GILBERT, E. P., and PETERSON, R. E. (1981).

Cardiovas-

cular teratogenicity of 2,3,7,8-tetrachlorodi-benzo-p-dioxin in
the chick embryo.

Toxicol. App1. P h armaco1. 61, 197-204.

ELOVAARA, E., HEMMINKI, K., and VAINIO, H. (1979).

Effects of

methylene chloride, trichloroethane, tetrachloroethylene and
toluene on the development of chick embryos.

Toxicology 12, 111-

119.

FRITZ, H., and BECKER, H. (1981).

The suitability of carboxymethyl-

cellulose as a vehicle in reproductive studies.

Arzn.-Forsch.

Drug Res. 31, 813-815.
GEBHARDT, D. O. E. (1972).
teratology.

The use of the chick embryo in applied

Adv. in Teratology 5_, 97-111.

KITOS, P. A., WYTTENBACH, C. R., OLSON, K., and UYEKI, E. M. (1981).
Precision delivery of small volumes of liquids to very young
avian embryos.

Toxicol. Appl. Pharmacol. 59, 49-53.

MISAWA, M., DOULL, J., KITOS, P. A., and UYEKI, E. M. (1981).
Teratogenic effects of cholinergic insecticides in chick embryos
Toxicol. Appl. Pharmacol. 57, 20-29.
MONIS, B., and RAVASIO, R. A. (1981). Teratogenic effect of lambdaCarrageenan on the chick embryo.

Teratology 23, 273-278.

SILKWORTH, J., MCMARTIN, D., DE CAPRIO, A., REJ, R., KUMAR, S., and
KAMINSKY, L. (1982).

Acute toxicity of soot from a polychlori-

nated biphenyl-containing transformer fire, (in preparation).

11

�SMITH, R. M. , O'KEEFE, P. W., HILKER, D. L. , JELUS-TYROR, B. L. , and
ALDOUS, K. (1981a).

Chemical analysis of 2,3,7,8-tetrachlorodi-

benzo-p-dioxin and 2,3,7,8-tetrachlorodibenzofuran in a soot
sample from the transformer explosion in Binghamton, New York.
N.Y. State Dept. of Health Report. Feb. 20, 1981.
SMITH, R. M., HILKER, D. L., O'KEEFE, P. W., KUMAR, S. , O'BRIEN,
J., JELUS-TYROR, B. L., and ALDOUS, K. (1981b).

Analysis of a

Binghamton soot sample for tetrachlorodibenzofurans and tetrachlorodibenzo-p-dioxins. N.Y. State Dept. of Health Report/
October 1, 1981.
SWARTZ, W. J. (1980).

Dissimilarities in the toxic responses of

early chick embryos to DDT administered in different vehicles.
Bull. Environ. Contam. Toxicol. 25, 898-901.
WILSON, J. G. (1978).

Review of in vitro systems with potential for

use in teratogenicity screening.

J. Environ. Path. Toxicol. 2,

149-167.
WORLD HEALTH ORGANIZATION, Techn. Rep. Ser. (1967) No. 364.

12

�Figure Legend
Fig. 1.

The embryo lethality of Binghamton soot as a function of

dose.

Soot was administered to fertile chicken eggs in 0.1 ml

0.75% aqueous methyl cellulose through a hole into the air sac on
day 4 of incubation.

The viability of the embryos was assessed

on day 18 of incubation.

13

�PERCENT LETHALITY
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