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                    <text>Item D Number

02233

Author

Gierthy, John F.

New York State Department of Health, Center for Labor

Report/Article fitto Typescript: Progress Report: Evaluation of In Vitro
Assays for the Detection of "Dioxin-Like" Activity in the
Binghamton State Office Building, May, 1983

Journal/Book Title
Year

1983

Month/Day

Ma 23

Color
Number of Images

v

D

9

Descrlpton Notes

Thursday, September 20, 2001

Page 2233 of 2293

�Progress Report: Evaluation of In Vitro Assays for the Detection of
"Dioxin-Like" Activity in the Binghamton State Office Building

by

John F. Gierthy
and

Gerald D. Frenkel

New York State Department of Health
Center for Laboratories and Research
May,

1983

RECEIVED
MAY 2 3 1983
DIRECTOR
PUBLIC HEALTH

�Progress Report: Evaluation of In Vitro Assays for the Detection of
"Dioxin-Like" Activity.in the Binghamton State Office Building. Gierthy,
J.F. and Frenkel, G.D. (May, 1983) Previous reports have described the
development and application of two in vitro systems for the detection
of "dioxin-like" activity in extracts of soot contaminated with polychlorinated dibenzodioxins and dibenzofurans. The cell keratinization system,
based on the induction of keratinization in epithelial cells by exposure to
2,3,7,8-TCDD, and the flat cell assay, based on a 2,3,7,8-TCDD induced
change in cellular morphology have both been shown to be potentially useful
in the detection of dioxin-like activity in extracts of soot from the
Binghamton State Office Building (BSOB).
Further verification of the specificity of the flat cell induction to
2,3,7,8-TCDD exposure has been carried out. Various polychlorinated
dioxins (PCDDs) and dibenzofurans (PCDFs), polychlorinated biphenyls
(PCBs), polynuclear aromatic hydrocarbons (PAHs), and pesticides have been
tested for their ability to induce the flat cell morphology. Results show
that 2,3,7,8-TCDD is the most potent inducer of this morphological change,
while the other PCDD and PCDFs have activity ranging from 10
to 10
of this isomer. The PCBsi,PAHs and pesticides had lower activity ranging
from 10
to less than 10
that of 2,3,7,8-TCDD. Where comparison was
possible, a good correlation was seen between the published relative activity of compounds in the keratinization system and their activity in the
flat cell assay. These results suggest that the sensitivity and specificity of the flat cell assay is similar to that of the keratinization
system.
Previously, benzene extracts of cotton gauze swipes from the BSOB were
found to contain a substance which precipitated during solvent exchange to
DMSO and resulted in a loss of activity in the bioassays. This substance
has now been found to be associated with the cotton gauze swipe pads.
Results show that pre-extraction of the gauze pads with benzene allows full
recovery of activity.

�1
Hyperkeratinization is considered to be responsible for the occurrence
of chloracne in humans exposed to polychlorinated dioxins and dibenzofurans (Poland et al_., 1982). This effect is thought to be caused by
an induced differentiation of the squamous epithelium.

In this regard,

2,3,7,8-tetrachlorodibenzo(p)dioxin (2,3,7,8-TCDD) is considered to produce
a sustained stimulation of a normal physiological response which leads to
chloracne (Poland e_t aK, 1982).

Knutson and Poland have used the in

vitro XB/3T3 cell keratinization system (Rheinwald £t ai., 1975) to
study this effect of chlorinated dioxin isomers and congeners (Knutson et
al., 1980). In previous reports (Gierthy e£ al., 1982a,b) we have
demonstrated the use of this system as an assay for the detection of these
compounds in Binghamton State Office Building (BSOB) soot extracts.
During these experiments, the appearance of an altered cell morphology
was observed in those cells which had been exposed to 2,3,7,8-TCDD or the
soot extracts (Gierthy £t al., 1982a,b). This change was first seen
after 7 days of exposure to the samples and was characterized by a flat
cell morphology as compared to the more fusiform cells in the unexposed
—11
cultures or those exposed to less than 10
M 2,3,7,8-TCDD. An apparent

cessation in cell growth was also seen in these cells, while the unexposed
cells continued to proliferate, resulting in more dense cultures.
The minimal concentration of each soot sample extract capable of
inducing the flat cell response was recorded as a measure of relative
activity.

The correlation between the concentration required for induction

of the keratinization response and the flat cell morphology (Gierthy et_
al., 1982a) indicated that it may be possible to use the flat cell
morphological change in these cells as an alternative and improved endpoint
in the assay for dioxin-like activity.

�The reproducibility of the assay as well as its ability to differentiate between various concentrations of 2,3,7,8-TCDD has been shown to be comparable to that of the cell keratinization system (Gierthy et al.,
1982b). Other cell lines, including fibroblasts and transformed epithelial
cells, were tested for their ability to respond to 2,3,7,8-TCDD with a
change in morphology, but no flat cell effect was observed.

Various inhibi-

tors of macromolecular synthesis and mitosis were examined for their
ability to induce flat cell morphological change.

As in the keratinization

system (Knutson et al^., 1980), all were found to be inactive over a
broad range of concentrations (Gierthy et^ a_^., 1982b), indicating that
the effect is not associated with general toxicity but may be a specific
effect, analogous to, and perhaps related to, keratinization.

This possi-

bility was supported by the finding that 2,3,7,8-tetrachlorodibenzofuran
(2,3,7,8-TCDF) also induced the flat cell effect (Gierthy et al.,
1982b), but had approximately one tenth the potency as 2,3,7,8-TCDD, which
is the relative potency which has been reported for these two compounds in
the induction of keratinization (Knutson et_ al_., 1980).
This report describes further experiments which have been performed to
establish the validity of the flat cell system as an assay for dioxin-like
activity, as well as preliminary studies regarding the application of the
in vitro assays to the detection of dioxin-like activity in surface swipe
samples taken from the BSOB.
Results and Discussion
Further Validation of the Flat Cell Assay
including polychlorinated dibenzo(p)dioxins

Studies on 24 chemicals,
(PCDDs), polychlorinated

dibenzofurans (PCDFs), polychlorinated biphenyls (PCBs), polycyclic
aromatic hydrocarbons, and pesticides have indicated at least a 63 million

�fold range in the potential of these compounds for inducing the flat cell
effect (Table 1).

These data show that the flat cell effect, like the

keratinization reponse, is by far, most sensitive to the more toxic PCDDs
and PCDFs with 2,3,7,8-TCDD being the most potent. Specifically,
1,2,4,7,8-penta-CDD, which lacks chlorination in one of the lateral
positions of one of the benzene rings shows 100 fold less activity than
2,3,7,8-TCDD.

2,3,7,8-TCDF was shown to be the most potent PCDF tested

and, as in the keratinization system (Knutson et^ al., 1980), had a flat
cell inducing activity an order of magnitude lower than 2,3,7,8-TCDD.
Other PCDFs tested gave a range of activity, with the hexa-CDF being more
potent than the octa- or di-CDFs. The range of activity observed for the
PCDDs and PCDFs tested, relative to 2,3,7,8-TCDD was about 1,000 fold.
This is contrasted by the activity of the various PCBs tested. Here the
flat cell inducing activity was 10 -10
2,3,7,8-TCDD.

times less potent than

Similar relative activity was reported in the keratinization

system for another halogenated biphenyl, 2,3,4,2',3',4'-hexabromobiphenyl
(Knutson e£ al., 1980).

The polynuclear aromatic hydrocarbons varied

in activity in relation to 2,3,7,8-TCDD.
benz[ajanthracene were about 10
2,3,7,8-TCDD respectively.

3

Dibenzo[a,h]anthracene and

4
and 10 times less potent than

This correlates well with the reported

activities of these compounds in the cell keratinization system (Knutson
et^ al^., 1980).

3-Methylcholanthrene and benzo(a)pyrene were both toxic

at concentrations which were insufficient to induce a significant flat cell
effect.

These compounds were found to be inactive as inducers of

keratinization in the XB/3T3 system (Knutson £t £1^., 1980). The
pesticides were all inactive in inducing the flat cell response at the
concentrations tested with the exception of Mirex which had the highest

�potency of this group (10 times less active than 2,3,7,8-TCDD).

These

data indicate that the specificity of the flat-cell assay appears similar
to that of the cell keratinization system.
Application to BSOB Samples

Versar New York Inc. (Springfield, Va.) has

supplied twenty-nine benzene extracts of soot samples from the BSOB for
preliminary testing of the bioassays.

These included benzene extracts of

cotton gauze swipes of BSOB surfaces, matrix blanks and reagent blanks.
Upon solvent exchange into DMSO, a precipitate was formed in all of these
samples except the reagent blank and therefore seemed to be associated with
the gauze pad extracts. Furthermore when the matrix blanks and reagent
blanks were spiked with 2,3,7,8-TCDD prior to solvent exchange, the
activity of spiked matrix blank samples was significantly lower than that
of spiked reagent blanks. The presence of a waxy precipitate was confirmed
by similar solvent exchange performed by Versar on the cotton gauze swipes
(Sonchik, 1982). Versar also noted that a PCS spike (Aroclor 1254, 1
ug/pad) partitioned into the precipitate, thus reducing the concentration
found in the DMSO.
Versar subsequently supplied benzene extracts of gauze pads which had
been pre-extracted with benzene. When these samples were solvent exchanged
as before no precipitate was observed in three samples and only a very
slight precipitate in one of the samples. Furthermore when these samples
were spiked with 2,3,7,8-TCDD prior to solvent exchange, full bioassay
activity was recovered.

No bioassay activity was found when unspiked

samples were tested.
From these results, it can be concluded that the precipitate which
formed during solvent exchange of the benzene extract of the gauze swipes
was a substance which had been extracted from the gauze.

This precipitate

�prevented full recovery of added 2,3,7,8-TCDD (as well as PCBs (Sonchik,
1982)). Pre-extraction of the cotton gauze pads with benzene effectively
removes this substance.

It appears that this procedure will allow further

studies to be done concerning the feasibility of using the in vitro
bioassays to detect dioxin-like activity in the surface swipe samples from
the BSOB.

�Table 1
Induction of the Flat Cell Effect by Various Chemicals
Minimum Detectable
Concentration (ppb)
2,3, 7,8-Tetrachlorodibenzo(p)dioxin

0.003Z
-=• ~\

l,2,4,7,8-Pentachlorodibenzo(p)dioxin

ro.359j&gt;

2,3, 7,8-Tetrachlorodibenzofuran

0.032

2,3,4,6,7, 8-Hexachlorodibenzof uran

0.378

Octachlorodibenzofuran

4.48

2,6-Dichlorodibenzofuran

&gt;2.38

3,4,3' ,4'-Tetrachlorobiphenyl

100

2,4,5,2' ,4' ,5'-Hexachlorobiphenyl

1,000

2,5,2' ,5'-Tetrachlorobiphenyl

&gt;10,000

2,3,4,2' ,4' ,5'-Hexachlorobiphenyl

&gt;10,000

2,3,4,2' ,3' ,4'-Hexachlorobiphenyl

&gt;10,000

Aroclor

1254

10,000

Dibenzo [a,h ]anthracene

10

Benz [a ]anthracene

100

&gt;iooa
&gt;iooa

3-Methylcholanthrene
Benzo(a)pyrene
6-Naphthoflavone

1,000

Pyrene

&gt;10,000

Mirex

10,000

Dieldrin

&gt;10,000

Aldrin

&gt;10,000

o.p'DDT

&gt;10,000

Lindane

&gt;10,000

a -BHC

&gt;200,000

a

Toxic concentration was 1,000

ppb.

�Literature Cited
Gierthy, J.F. and G.D. Frenkel (1982a) A Preliminary Report "on the
Evaluation of an In Vitro Assay for the Detection of "Dioxin-Like"
Activity Using Extracts of Soot from the Bingharaton State Office
Building.

New York State Department of Health Report.

Gierthy, J.F. and G.D. Frenkel (1982b) Progress Report:

March, 1982.

Evaluation of an

In Vitro Assay for the Detection of "Dioxin-Like" Activity in the
Binghamton State Office Building.
Health Report.

New York State Department of

October, 1982.

Knutson, J.C. and Poland, A. (1980). Keratinization of mouse teratoma cell
line XB produced by 2,3,7,8-tetrachlorodibenzo-p-dioxin:

an in vitro

model of toxicity. Cell 22, 27-36.
Poland, A. and Knutson, J. (1982) 2,3,7,8-tetrachlorodibenzo-p-dioxin and
related halogenated aromatic hydrocarbons:

Examination of the

mechanism of toxicity. Ann. Rev. Pharmacol. Toxicol. 22, 517-554.
Rheinwald, J.G. and Green, H. (1975). Formation of a keratinization
epithelium in culture by a cloned cell line derived from a teratoma.
Cell 6, 317-330.
Sonchik, S. (1982). Analytical Report:

Removal of Interferences of

Samples for Cell Keratinization Assay.

1982.

Versar Report, December 8,

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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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