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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;
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                <text>Contamination of an Office Building in Binghamton, New York by PCBs, Dioxins, Furans,and Biphenylenes After an Electrical Panel and Electrical Transformer Incident</text>
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°2287

Author

Schecter, Arnold

Corporate Author
ROpOrt/ArtlGlO TltlB Typescript: Transient Liver Pathology in Patients
Consuming Water from a Private Well Contaminated by
PCBs from a Submersible Water Pump, [nd]

Journal/Book Title
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Month/Day
Color

D

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6

DOSCrlPtOll NOtBS

Typescript of article published in Chemosphere, 1987, vol.
16, no.1,pp.37-42.

Thursday, September 20, 2001

Page 2287 of 2293

�TRANSIENT LIVER PATHOLOGY IN PATIENTS CONSUMING WATER FROM
A PRIVATE WELL CONTAMINATED BY PC3s FROM A SUBMERSIBLE WATER PUMP

Arnold Schecter
Department of Preventive Medicine
Upstate Medical Canter
Clinical Campus
State University of New York
Binghamton, New York 13901
ABSTRACT

Submersible water pumps in private water wells have in some instances been found to
contain PCBs in their oil. When these pumps leak they may release PCSs into the drinking
water constituting a potential health hazard.
IHTROOUCTIOH

Since 1982, in New York State, and in Wisconsin, a number of private water wells,
usually in rural areas, have been found to be contaminated with PCBs. The source of this
contamination is thought to be submersible water pumps from several manufacturers where
PCBs were apparently, found in the oil of the pumps or in their capacitors. Although the
manufacturers deny Intentionally putting PCBs in these pumps, the presence of PCSs has been
documented by State and County Health Departments from 1982 through 1985 in Broome County
and adjacent areas in Upstate New York as well as in Wisconsin. PCB levels in drinking
water from these wells has been found to be as high as 57 times greater than State PCB
drinking water standards at this time. Whether significant health consequences occur
depends on the Ingested dose of specific PCS isomers with their usually coexisting
chlorinated dibenzofurans and less frequently coexisting chlorinated dibenzo-p-dioxins.
A medical case study with transiently elevated liver enzymes found in three members of a
family after ingestion of PCBs 1n their drinking water is presented.
FINDINGS
A family of three came to the Upstate Medical Center affiliated Faculty Practice
Occupational Medicine Clinic in Binghamton, New York, located at Binghamton General

�Hospital, with.complaints of feeling sick from documented ingestion of PCBs in their
drinking water for at least one week, with accompanying subjective, primarily central
nervous system, symptoms of discomfort, a feeling of generalized illness and "dizziness".
The family members had noted a chemical odor and a film on the water at times. A Health
Department investigation had determined that the source of PCBs and a chemical taste in their
water was a submersible water pump of a type shown in Figures 1 and 2, which had been
leaking. The pump in question, a Barnes pump from the Barnes Manufacturing Co. of Mansfield,
Ohio and Oakland, California, had detectable PCBs when tested by the State Health Depart{12}
ment.v ' ' Upon review of Health Department records, it was found that Peabody Barnes Pumps
were found to have PCSs which leaked in nine instances between 1982 and 1985. ' ' Some
pumps were found to have 2.5% PCBs in their oil, when tested by the State Health Department.
In the pump owned by the patients in this case study, there was a finding of 6.6 parts
per billion of PCBs in the drinking water. The leaking pump oil was found to have 630,000
parts per billion of PCBs. Analysis for polychlorinated dibenzofurans which so frequently
accompany PCBs was not performed.
Patients with PCS contaminated water noted bad odors, peculiar taste, a petroleum-like
taste, and a disorientation or "spaced out" feeling after drinking the water. Serum PCB
levels in the three patients followed by us, a mother, father and 12 year old son, seen
one month after the consumption of water contaminated with PCBs were quite low, below 2 ppb;
whereas serum PCB values for adults from this part of Upstate New York are usually about
5-10 ppb. The family's diet was somewhat unusual in that they usually ate "natural" foods,
usually vegetables, and also Ingested high levels of vitamins. Abnormal (elevated) liver
enzymes were found in blood tests performed on all three members of this family who ingested
the PCS contaminated water for an estimated one weak. These abnormal values, indicative of
liver damage, returned to normal levels within one month after the initial values were
documented, or two months after ingestion of water contaminated with PCBs, suggesting that
the acute injury was a transient one. No clinical or laboratory evidence of hepatitis
or drug induced liver damage was found. The patients recovered from their acute
medical problems but are being followed for possible delayed onset pathology.
New York State "Safe Drinking Water Guidelines" for PCBs is one part per billion.^
Water from wells contaminated by oil from these pumps, schematically diagramed in Figures 2,
3, and 4, have shown between .26 and 57 parts per billion, according to State records. '
Tests of the oil from the contaminated pumps have shown 630,000 to 24,000,000 parts per
billion of PCBs. Tests of the lubricating oil fn these pumps have shown that levels of
PCBs have been found in pumps more than 20 years old and as new as a 1982 model. To date
the brands of pumps Involved have been Barnes or Peabody Barnes, Reda and Myers, (2^
'
According to the Water Systems Council, Inc,, SOS of private well pumps are above
ground units and the remaining 50% are submersible units. Half are oil cooled and half
are water cooled. Census figures for 1982 describe 12,000,000 homes connected to private
wells in the U.S.A.^
By way of comparison, the U.S. Food and Drug Administration sets a 2 parts per million
PCB tolerance level for fish consumption. The P.O.A. recommends eating fish at this level

�Check valve
Radial bearing

Impellers

Pump Intake
Seal

Electric motor
Pressure equalizing tube

I Thrust and radial bearing
Fluid chamber

Fig. 2 - This schematic diagrams the internal components
of a submersible water pump.

Fig. 1 - A Health Department technician is shown holding
a PCB contaminated submersible water pump.

�\

150'OF DISCHARGE PIPE
WITH 2 - 90° ELBOWS
PUMP

Fig. 3 - A typical arrangement of a submersible water pump,
well, and pipe fixtures leading to a hone Is shown here.

�no more than once per week. ' A half pound or eight ounce serving of fish contaminated at
this limit would contain 500 nricrograms of PCBs.

win. SEAl

SlfjDC* V A L V E '

•

AI» INTAKE VAIVE !/•;.%
:.:••

if NO CHAIN is AVAIIA»U

MQTO»

\-J

Fig. 4 - This schematic depiction details the apparatus
immediately related to the pump and well.
Also, for comparison, if two liters of water at the New York state Drinking Water PCS
Guidelines are consumed for 70 years with a one part per billion PCS level this has been
calculated to lead to one additional cancer death per 10,000 persons according to State
(a)
Health Department calculations. '
Additional concern has been raised by an EPA study performed under contract by Versar,
Inc., of Springfield, VA, in 1980 which estimated that 1,100,000 wells may have PC8 capacitors in the well motors. ' This is different from the current findings of PCBs in the
oil of the motors or pumps themselves, rather than the capacitors.

�SUMMARY AND RECOMMENDATIONS

Submersible water pumps in private wells are widespread, especially in rural areas, and
may constitute a potential health hazard, especially if they contain PCSs with the usually
concomitant chlorinated dlbenzofurans and occasional chlorinated dibenzo-p-diox1ns. These
leaking pumps have been demonstrated to contaminate drinking water above levels considered
safe for human consumption, PCBs apparently were used in these pumps from at least three
known manufacturers at least in the United States without the admitted knowledge of the
l&amp;\
presence of PCSs, except in the capacitors, by any party/ ' The extent of these contaminated pumps remain to be documented. To date the only incidents known to us are the nine
pumps 1n and around the Broome County, New York area, where the public and health department are especially sensitive to the possible presence of PCBs since the PCS, dloxtn and
furan contaminated State Office Building incident of February 1981, ' and In Wisconsin where
the Wisconsin Department of Natural Resources (WONR) has also detected PCB contamination in
private well water with submersible water pumps as the probable source. It is unclear as
to whether only the capacitors contain PCBs or whether the pump oil Itself, usually
pharmaceutical grade mineral oil, also contains PCBs. News releases to the public and a
notice to well drillers and installers have been issued 1n Wisconsin by the WONR. Further
sampling of lubricating oil from additional pumps and water from more wells 1s planned 1n
Wisconsin. However, the nationwide distribution of these pumps suggests that other Instances
will be documented when the possibility of PCB contamination exists in similar submersible
water pumps.elsewhere in the world. Because of the large number of such pumps In the United
States and worldwide, it is possible that these may constitute a potential human health
hazard. Further chemical testing of suspect pumps and water 1s Indicated and appropriate
medical evaluation of patients exposed to PCS contamination is Indicated, including routine
blood screening tests as well as blood PCB levels, serially'obtained wherever the possibility
of a transient elevation above the patient's baseline exists.
REFERENCES
1.
2.
3.
4.
5.
6.
7.

Personal communication, Broome County Health Department.
Personal communication, Environmental Health Division, New York State Health
Department.
Mew York State Safe Drinking Water Guidelines, 1984.
The Sunday Press, Odato, J.M., July 7, 1985; The Evening Press. OdatO, J.M.,
July 8, 1985; Press &amp; Sun-Bulletin, Odato, J.M., December 8 &amp; 11, 1985.
U.S. Food and Drug Administration Guidelines for Consumption of PCB Contaminated
F1sh, 1982.
Woodcock, 8. and Powers, P., (Versar, Inc.), PCB Contamination of Well Water: An
Engineering Risk assessment, U.S. EPA Document EPA-570/9-SQ-OQ1, January 1982.
Schecter, A., Contamination of an Office Building in Blnghamton, New York by PCSs,
01ox1ns, Furans and Biphenylenes after an Electrical Panel and Electrical Transformer Incident, Chemosphere, 12, (4/5), 669-680, Pergamon Press Ltd., London,
1983.

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                    <text>Item D Number

°2285
Schecter, Arnold

Corporate Author
Report/Article Title Typescript: The Binghamton State Office Building PCB,
Dioxin and Dibenzofuran Electrical Transformer
Incident: 1981-1986, [nd]

Journal/Book Title
Year
Month/Day
Color

D

Number of Images

8

Descrtaton NOtBS

Typescript of chapter published in: Crummett, O., et al,
Chlorinated Dioxins and Related Compounds, 1986, vol. 15,
no. 9-12, pp. 1273-1280.

Thursday, September 20, 2001

Page 2285 of 2293

�THE BINGHAMTON STATE OFFICE BUILDING PCS, OIOXIN AND DIBENZOFURAN
ELECTRICAL TRANSFORMER INCIDENT:

1981-1986.

Arnold Schecter
Department of Preventive Medicine, Upstate Medical Center, Clinical Campus,
State University of New York, Binghamton, New York 13901
ABSTRACT

The Binghamton State Office Building (BS08) polychlorinated biphenyl (PCS) and chlorinated
benzene containing electrical transformer arcing and fire incident of February 5, 1981, was
the first recognized incident of its kind. A surge of excess electricity led to an electrical
panel malfunction at 5:30 AM. For about 30 minutes intense heat was generated as electrical
arcing occured. Dense smoke containing polychlorinated dibenzofurans (PCDFs) and
polychlorinated dibenzo-p-dioxins (PCODs) as well as biphenylenes billowed up through air
shafts and contaminated all areas of the building later tested for these chemicals. This
incident was the first outside a laboratory setting to demonstrate the conversion of PC3s, in
the presence of oxygen and heat, to PCDFs, and of the chlorinated benzenes to PCODs. It
demonstrated a hitherto unsuspected potential health hazard of PCS and chlorinated benzene
containing electrical transformers, and by implication, capacitors, when not properly separated
from areas of buildings used by workers and public. The building has been shut since then and
an estimated £40,000,000 may be spent on direct cleanup and rehabilitative costs prior to
reopening of the building, if it is to be reopened. Elevated levels of serum PC8s were
detected in workers, eg., firefighters initially involved in the fire, which stabilized at
lower levels later in the year. Elevated penta- and hexa- chlorinated furan isomers
corresponding to Isomers found in the soot (and identical to some Yusho Isomers) were found
in some cleanup workers. Electron microscopy of percutaneous liver biopsies of three patients
chemically exposed from the incident showed lesions similar to those seen 1n guinea pigs fed
the soot, which was biologically quite active. This incident, and others occurring afterward,
has led the US Environmental Protection Agency to ban PCS containing transformers from similar
buildings.
INTRODUCTION
On February 5, 1981 an electrical malfunction in a modern, 18 story office building led
to overheating of a transformer in the BSOB, Binghamton, New York, about 180 miles northwest
of New York City. Between 180 and 200 US gallons of transformer fluid leaked from the overheated
transformer in a basement of the building. This fluid originally was constituted as a 6S%
Arochlor 1254 and a 35X tri- and tetra- chlorinated benzene containing mixture. Due to an
unusual arrangement of air shafts, ducting and air handling systems the entire building was

�contaminated, Including hidden spaces under floors, spaces above false ceilings, and inside
air ducts (1,2). Initial sampling showed the soot to be 5% PCS in content. In addition,
2,168,000 parts per billion (ppb) of PCDFs, 20,000 ppb of PCDOs as well as 50,000 ppb of
chlorinated biphenylenes were also found in soot samples.
Since that time the building has been subject to a variety of cleanup efforts. During
the first few weeks after the accident, several hundred workers were exposed to the chemicals
by virtue of being involved as office workers, cleanup workers, electricians, police,
firefighters, security workers and, initially, firefighters and police. Lawsuits were filed,
or the intent to sue was initiated, in some instances possibly to not lose the right to
eventual lawsuit, should Injury from chemicals develop at a later date. Under present New
York law, a lawsuit must be filed within three years after the incident-net the injury or
illness-or the statute of limitations precludes initiation of lawsuits. The Mew York State
legislature is considering changing this law which predates an understanding of the latency
period involved in some chemical injuries, especially in the case of carcinogens or reproductive
toxins, such as those involved in this incident.
As a result of the Binghamton Incident, and others which followed, the United States
Environmental Protection Agency (US EPA) has ruled that PCS containing transformers must be
phased out in several years in many public buildings. Their action was based partially on
economic considerations, as well as on health considerations.
The 3S03 was constructed less than twenty years ago at a cost of 17 million dollars.
Its total cleanup costs are estimated to be 40 million dollars, including replacement of
furnishings. Certain hidden spaces will be cleaned and others will not. Estimated time of
opening is in 1987, 6 years after the incident.
RESULTS
Toxlcoloqical findings (3-5) include the following: The 8SOB soot does not Inactivate the
chemicals as determined by guinea pig bioassays. For example, the rate of cancers is increased
in animals fed the BSOB soot as compared to control animals. Electron microscopic findings
in liver cells were similar to those previously described in animals or persons exposed to
PCSs, PCDFs or 2,3,7,8 TCOO. The toxicity of this mixture appears to be to a large extent due
to the level of 2,3,7,8 substituted penta- and hexa- chlorinated dlbenzofurans. The 8S08
soot but not fireplace soot or charcoal used as controls lead to malformations in chick embryos
as well as decreased viability.
Human findings from Singhamton exposed patients include the following (5-10): Elevated serum
PCS levels which returned to normal levels within one to two years in some patients including
firefighters involved with the fire, with a match of the PCS isomers found 1n soot and adipose
tissues, in some cases. Elevated PCOF levels in some exposed patients as compared with
Singhamton controls were found, as were elevations of specific Isomers of PCDFs in fat tissue
which corresponded to isomers identified 1n the BSOB soot. Some of the penta- and hexachlorinated PCOFs were the same as found in Yusho patients in Japan. Control 8S08 adipose
tissue samples revealed, for the first time, the high level of PCDOs and PCDFs In the general
US population, around 1,000 to 1,200 ppt on a wet weight basis. These were 2,3,4,7,8, PCOF,
1,2,3,4,7,3 PCDF and 1,2,3,6,7,8 PCDF. Transient serum liver enzyme elevations were found

�in some patients as were elevations of triglycerides and cholesterol levels in serum taken
shortly after the exposure. These usually returned to normal levels within one year after
the incident. Three patients suffered from prolonged elevations of liver enzymes for which
no cause other than the chemical exposure could be found. These three patients-exhibited
similar ultrastructural alterations to those seen in animals dosed with PCBs, 2,3,7,8 TCDO,
the BSOB soot, or in humans exposed to chlordecone (Kepone) (11) or the Yusho rice oil incident
(12) Lipid droplets were found in the hepatic parenchyma! cell cytoplasm, as was a slight
increase in smooth endoplasnric reticulum. Glycogen was plentiful. Mitochondria were
pleomorphic or deformed and giant mitochondria were present. Some cristae lined up parallel
rather than perpendicular to the long axis of mitochondria and crystalline structures were
found in other mitochondria. Large, dense, electron Intranritochondrial granules were seen
in many mitochondria. In addition, several cases of sic in cancer, including one malignant
melanoma, were found in exposed workers. Several suicides were reported in the original group
of approximately 500 potentially exposed persons, in or near the building in February 1981.
Risk assessment calculations for reentry into the building, and "acceptable daily intakes"
(AOIs) of PCODs and PCDFs were calculated, possibly for the first time for a building, as part
of the SSOB's reentry criteria. The calculations were derived from rat one nanogram per kg
per day no effect levels (NOELs) for 2,3,7,3 TCOO. Rats, being intermediate in sensitivity,
were chosen rather than the more sensitive guinea pigs, and a safety factor of 500 fold was
applied. An assumption was made that other sources of intake such as food or air need not
be factored into this equation; rather, that only 8S08 air levels and soot levels of PCODs
and PCDFs (but not PCBs to date) need to be considered. Conversion to "2,3,7,8 TCDD equivalents"
for other PCDD and-PCDF isomers was employed and a review of the sparse scientific literature
was used for conversion factors. Recently, work by Nagayama and associates suggests that
conversion factors based on enzyme induction studies- in animals may underestimate toxldty
to humans (13). At any rate a 2 picogram/Kg/day is considered an AOI for 2,3,7,8 TCOO
equivalents, calculated by the New York method or 10 pg 2378 TCDD equivalents/I^ of air and
25 ng/M2 surface for office worker reentry. The New York approach 1s considerably less
conservative than the California method, which assigns an equal potency to all tetra- to hepta
2,3,7,3 chlorine substituted dloxlns and dibenzofurans rather than weighting downwards the
higher chlorinated PCODs and PCOFs.
This difference is apparent in Table I, modified from New York State BSOB records. It
can be seen that using the California method of calculation we have 40 pg/M^ of "2,3,7,8 TCDO
equivalents" in the air, well above the allowed 10 pg amount for reentry, but using the New
York State Health Department method of calculating dloxin equivalents we find a 7.5 pg/M^ air
level, within the level for reentry for workers without protective gear. Despite an apparent
similarity in the "dloxin equivalents", 10 pg/M^, used by the New York and California Health
Departments, the method of calculation is very different. A further difficulty can be
appreciated in Tables II and III. In Table II two highly qualified chemical laboratories
analyzed the same sample or a split sample and come up with as much as 17:1 fold differences
(2,000 vs 120) or 1:5 fold differences (5,900 vs 29,500) in furan levels, in some instances.
In Table III two highly qualified laboratories varied from each other by a factor of from 1.3
to 6.3 fold. Thus, if one cannot be certain of the exact amounts of specific isomers of dioxins

�or furans present, there is a further major difficulty in calculating safety for reentry.
Few laboratories are able to perform analyses for mixtures containing many isomers because
of technical difficulties including chemical cleanup problems, separation difficulties, lack
of available chemical standards, and the many chemical interferences possible. In addition
the proper GC/MS equipment is needed. Cost is high and turnaround time quite slow at present.
Laboratory charges vary from $500 to $2,000 per analysis depending on the number of samples,
their difficulty and the analyses desired; average turnaround time is measured in months.
Contamination levels of the building after several years of cleaning, usually by repeated
washing with steam or water and detergent rather than by removing and replacing walls, floors,
and lighting fixtures, can be seen in Tables IV and V. what is noteworthy here 1s the uneven
results from this method of cleaning, even after four years and 30 million dollars of cleanup
effort, wi, W2, etc., refer to locations and, usually, a floor number.
CONCLUSIONS AND DISCUSSION

The 8SOB contamination of an office building was the first of its kind to be Identified.
It has provided a rich learning experience with respect to medical, legal, insurance, cost,
chemical, toxicological and cleanup (vs. dismantling) issues. The unexpected health hazards
related to PCS transformers were first documented here, by human and animal data, from the
chemically contaminated soot and air. The costs associated with such defective design and/
or maintenance problems as found in the 8S08 were also first documented here. Weaknesses in
the New York State legal system with respect to a three year statute of limitations after an
incident, rather than after onset of illness, presenting problems for potential plaintiff and
defendant alike with respect to chemicals which may cause illness after a latent period, are
well documented here. Potentially affected workers must file law suits in that period of
time, during which no illness may exist, or forever lose the right to sue later, possibly
after the development of cancer or an adverse reproductive outcome occurs, which may or may
not be linked to the chemicals of exposure.
The use of fat biopsies for determining whether there is or is not an increased body
burden of PCODs or PCDFs after such incidents was first documented here, as was the use of
liver biopsy ultrastructural analysis as a sensitive although not specific marker of exposure
to -dioxlns and related compounds. The usefullness of serial serum PCS measurements in
documenting ingestion of PCBs after such acute exposures was documented in Singhamton, as it
was previously in the Yusho PC3/PCDF incident. The high level of PCOOs and PCDFs in the
general population was unexpected.
Difficulties in cleanup techniques and the difficulties in chemical analysis of the
Isomers involved has been documented by this incident, as have the difficulties of risk
assessment and determination of reentry criteria.
The extent of the health hazard posed to persons working in PCS, PCQF and PCOO contaminated
buildings is not yet clear. It is only by following exposed workers over time, accurately
estimating their exposure, and using a suitable control group that this question will be
answered. Special health problems may be posed to the fetus or a nursing newborn if the
mother works in such a building. These chemicals are transferred through the placenta and also

�in breast milk. The Infant may have a more sensitive immune system than an adult, and the
effect of a given level of these chemicals may be greater because of the infant's small size
and the long period of time which the chemicals will remain In the body (of a fetus or newborn)
as compared to an adult. The intake of PCBs, PCOOs and PCDFs from other sources, such as
food, also must be considered. It is possible, based on current knowledge, that current risk
assessments either overestimate or underestimate potential human health hazards. What is clear
is that it is possible to take steps to minimize human exposure to these toxic compounds.
REFERENCES
1. Schecter, A.J., Haughie, Q.F., and Rothenberg, R. PCS transformer fire ~ Binghamton, New
York. Morbidity and Mortality Weekly Report 30: 187-193 (May 1, 1981).
2. Schecter, A. Contamination of an office building in Bingnamton, New York, by PCBs,
dioxins, furans and biphenylenes after an electrical panel and electrical transformer
Incident. Chemosphere 12: 669-680 (1983).
3. Silkworth, J., 0. McMartln, A. DeCapHo, R. Rej, P. O'Keefe, and L. Kaminsky, 1982.
Acute toxicity in guinea pigs and rabbits of soot from a polychlorinated, biphenylcontaining transformer fire. Toxieol. Appl. Pharmacol. 65: 425.
4. Turner, J. and 0. Collins, 1983. Liver morphology in guinea pigs administered either
pyrolysis products of a polychlorinated biphenyl transformer fluid or 2,3,7,8-tetrachlorodibenzo-p-dioxin. Toxlcol. Appl. Pharmacol. 67: 417.
5. OeCaprio, A.P., O.N. McMartin, J.8. SJTkworth, R. Rej, R. Pause, and L.S. Kaminsky. 1983.
Subchronic oral toxicity in guinea pigs of soot from a polychlorinated biphenyl-containing
transformer fire. Toxicol. Apgl. Pharmaeol. 68,2: 308.
6. Schecter, A., Schaffner, P., Tiernan, T., and Taylor, M.: Ultrastructural alterations of
liver mitochondria after exposure to dioxins, furans, PCB's and biphenylenes. Banbury
Report 18: Biological Mechanisms of Dioxin Action. Cold Spring Harbor Laboratory,
Banbury Center Publications, pp. 177-189, 1984.
7. Schecter, A., Tiernan, T., Schaffner, F., Taylor, M., Gitlitz, G., Van Ness, G.F., Garrett,
J.H., and Wagel, O.J.: Patient fat biopsies for chemical analysis and liver biopsies for
ultrastructural characterization after exposure to polychlorinated dloxfns, furans and
PCBs. Environmental Health Perspectives, 60:241-254, 1985.
8. Schecter, A. and Tiernan, T.: Occupational exposure to polychlorinated dioxins, polychlorinated furans, polychlorinated biphenyls and biphenylenes after an electrical panel
and transformer accident in an office building 1n Slnghamton, New York. Environmental
Health Perspectives, 60:305-313, 1985.
9. Schecter, A., Tiernan, T.O., Taylor, M.L., Van Ness, G.F., Garrett, J.H., Wagel, O.J.,
Gitlitz, G., Bogdasarian, M.: Biological markers after exposure to polychlorinated
dibenzo-p-d1oxins, dibenzofurans, biphenyls and biphenylenes, Part I: Findings using
fat biopsies to estimate exposure. In: Chlorinated Dioxins and Oibenzofurans in the Total
Environment. Part II. Eds., Keith, L. Choudhary, G., and Rappe, C., Butterworth Publishers,
Stoneham, Massachusetts., Ann Arbor Science, pp. 215-245, 1985.

�10. Schecter, A., Ryan, J.J., Lizotte, R., Sun, W.-F., and Miller, L.: Chlorinated dibenzo
dioxin and dibenzofurans in human adipose tissues from exposed and control New York State
patients. Chemosphere. 14_: 6/7 pp. 933-937, Pergammon Press Ltd., Oxford, 1985.
11. Guzelian, P.S., G. Vranian, J.J. Boylan, W.J/ Cohn, and R.V. Blanke. 1980. Liver structure
and function in patients poisoned with chlordecone (Kepone). Gastroenteroloqy 8:206.
12. Nishlzumi, M. 1970. Light and electron microscope study of chlorobipheny poisoning. Arch.
Environ. Health 21: 620.
13. Nagayama, J., Kiyohara, C., Masuda, Y., and Kuratsune, M.: Inducing potency of arylhydrocarbon hydroxylase activity 1n human lymphoblastoid cells and mica by polychlorinated
diben-zofuran congeners. Environ. Health Perspec. 59: 107-112, 1985.

BINGHAMTON STATE OFFICE BUILDING 1984
CALCULATIONS OF AVERAGE "2,3,7,3-TCDD EQUIVALENTS"
DUE TO VARIOUS DIBENZOFURANS, DI8ENZODIOXINS AND BIPHENYLENES FOR
6TH AND UTH FLOOR AIR SAMPLES (MODIFIED FROM NEW YORK RECORDS)
NEW Y O R K C A L I F O R N I A
CALCULATION
CALCULATION
BEST ESTIMATE
RELATIVE ACTIVITY
RELATIVE ACTIVITY
OF AVERAGE
X OF COMPOUND CLASS X DUE TO CHLORINE
«
CONCENTRATION
VS. DIBENZODIOXINS
SUBSTITUTION
2.3,7-8 TCOF
8 pg/M-i

"2,3,7,8-TCOO EQUIVALENTS"

1/3

X

1

»

2.7 pg/M3

8 pg/M3

1/3

X

1

»

4. 7. pg/M3

14 pg/M3

1/3

X

1/30

*

0.1 pg/M3

13 pg/M3

TOTAL

X

7.5 pg/M3

40

PENTA CDFs:
12378 +12348
+23478
HEXA CDFS;
9 pg/M-3

X

TABLE I
I

COMPARISON OF 8ATTELLE VS. NEW YORK STATE DEPARTMENT OF HEALTH (NYSDOH)
2,3,7,8TCOF

TOTAL
TCDF

TOTAL
PENTA
CDF

TOTAL
HEXA
CDF

5,900

45,000

99,000

41,000

BSOB WIPE, STAIR TREAD
PCDD W-14 (BATTELLE)
FLOOR 16-17

29,500

145,000

117,000

60,700

BSOB WIPE, VINYL WALL
W-7 (NYSOOH 43969)

1,100

13,000

3,500

2,000

BSOB WIPE VINYL WALL
PCDO W-6 (BATTELLE)

1,320

4,980

820

120

Sample
BSOB WIPE, STAIR TREAD
PCDD W-13 (NYSDOH 43968)
FLOOR 16-17

�TABLE III
BINGHAMTON STATE OFFICE BUILDING
TEST PLAN: MEASUREMENTS OF RESIDUAL CONTAMINANTS REPORT
SEPTEMBER 5, 1984
POLYCHLORINATED OIBENZOFURAN ANALYSIS LABORATORY COMPARISON
(SINGLE EXTRACT)
CHLORINE NUMBER
(ISOMER)
2,3,7,3-TCDF
TETRA
PENTA
HEXA
HEPTA
OCTA

STALLING 1981

(lag/g)

RAPPE 1981

(ug/g)

FACTOR

12
28
670
965
460
40

3.2
5.1
6.3
1.9
4.5
1.3

3.7
5.4
107
512
102
30

TABLE IV
BINGHAMTON STATE OFFICE BUILDING
JANUARY 25, 1985 NEW YORK STATE REPORT
RESULTS OF PCB-12S4 SURFACE WIPES COLLECTED IN THE 8S08, SEPTEMBER 1984
TYPE OF SURFACE
FLOORS (MASTIC)

STAIRWELL TREADS
PAINTED LIGHT
FIXTURES (UPPER)

FLOOR

3
6
13
17
5
10
15
18
7-8
17-13

LOBBY CORE
LOBBY CORE
LOBBY CORE
LOBBY CORE
WEST/OUTER
WEST/OUTER
WEST/OUTER
WEST/OUTER
EAST
EAST

4
3
10
16
3

WEST/OUTER
WEST/OUTER
WEST/OUTER
WEST/OUTER
NEAR CORE
NEAR CORE
NEAR CORE
NEAR CORE

6

CONCRETE-MEN'S
RESTROOM CHASE

LOCATION

12
17
2
13

CONCENTRATION
(U9/M2)

AVERAGE
(H9/M2)

S.d.

55.00

65.2

19.25

11.2

66.5

76.6

31.75

45.5

19.75

6.3

lo
45
15
150
10
1
1
34
22
13
120
100
10
3
9
26
21
10
22
7
42

24.5

24.7

�TABLE V
BINGHAMTON STATE OFFICE BUILDING
JANUARY 25, 1985 NEW YORK STATE REPORT
(1984) DATA)
QUANTITY OF PCDF. PG/M^ (LIMIT OF DETECTION)
SAMPLE

2,3,7,8-Tetra

Tetra

Penta

Hexa

Hepta

Octa

(37)
90
(10)
1970
310
320

(80)
18
170
620
(13)
120

(503)
(554)
(119)
(226)
(205)
(58)

(1340)
361
(650)
(1185)
(463)
(285)

(211)1
(3244)
(347)
(274)
60300
55800

461091
(5015)
(979)
(495)
26800
37200

PCOD
PCDD
PCOD
PCDD
PCDO
PCDO

Wl
-W2
W3
W4
W5
M6

520
250
1720
2940
1450
1320

1200
345
2980
6160
3690
4980

PCDO
PCDO
PCDD
PCOO
PCDO
PCDD

W8
W9
W10
Mil
W12
W14

16200
7390
(20)
87
16500
29500

55500
36400
(20)
153
125000
145000

10400
240
56
48
136000
117000

1040
5580
20
(8)
128000
60700

PCDD
PCDD
PCDD
PCDO
PCDD
PCDD

W15
W16
W17
W18
W19
W20

3590
61000
287
88
4400
27300

51100
331000
639
213
14800
75900

46000
341000
240
130
9130
40500

26000
222000
40
(6)
870
9890

22600
136000
(268)
(233)
3200
28300

14200
100000
(601)
(777)
2360
7480

(7)
(9)
(103)
(5)
(4)

(31)
(75)
(74)
(24)
• (11)

(114)
(375)
(280)
(87)
(29)

PCDD W21ns2
PCOD W21fb
Lab Blank

Lab Blank
Lab Blank

1
2

3760
(24)
(26)
(4)
(2)

3760
(24)
(26)
(4)
(2)

(4)
(10)
(23)
(4)
(7)

Calculated using TCDD-^Ci? due to Interferences at M/Z 472
Spiked with 5 NG of 2,3,7,8-TCOF

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