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                    <text>Item D Number

°2293

Author
Corporate Author
RepOrt/ArtlOlB Tltlfl Typescript: The Role of the Office of General Services
and its Consultant, Versar Inc., in the Decontamination
of the Binghamton State Office Building, [nd]

Journal/Book Title
Year

Month/Day
Color

D

Number of bnagee

*

DOSCrlpton NOtBS

Note on 1st

Thursday, September 20, 2001

Pa9e; From: Glenn E. Haughie, M.D.

Page 2293 of 2293

�THE ROLE OF THE OFFICE OF GENERAL SERVICES
AND ITS CONSULTANT, VERSAR INC.
IN THE DECONTAMINATION OF THE BINGHAMTON STATE OFFICE BUILDING

The Office of General Services is responsible to the Governor for the
development and administration of operations and activities required to support
State agencies.
In this regard, OGS is responsible for the overall management of major
office building facilities throughout the State, including Binghamton,
New York.
The Office of General Services also provides architectural/engineering and
construction management services through its Design and Construction Group in
regard to State buildings and ancillary facilities. Since the February 1981
fire at the Binghamton State Office Building, the Design and Construction Group
has been primarily responsible for the administration of the decontamination
project and has been responsible for the oversight of the activities of
Versar Inc., the State's retained consultant for this project.
The involvement of the Design and Construction Group began with an emergency
response on February 5, 1981 as a result of the fire and ensuing power failure
which created a construction type emergency condition. At that time, measures
were taken to furnish temporary power to the building to replace the destroyed
electrical distribution system and also to commence preliminary cleanup
operations.
Shortly after the February 5 incident, the Office of General Services
identified the need for a personal representative of the agency's Commissioner
and Executive Deputy Commissioner to manage ongoing aspects of the project
related to intergovernmental coordination, general administration, and media
management for the project. A new position of Executive Coordinator was
established and was filled in June 1981. The incumbent of this position is
based in Albany but spends at least one day a week in Binghamton to ensure
that the concerns of the local levels of government as well as those of all
interested groups are addressed. Additionally, the Executive Coordinator ensures
that the Commissioner and Executive Deputy Commissioner are fully aware of all
ongoing aspects of the project, especially those matters which may require their
personal attention.
Since that time, the Design and Construction Group has been assigned
responsibility for four areas of the building's rehabilitation; namely, retention
of Versar Inc. as the State's consultant, the coordination, for review and approval,
of various plans and research developed by Versar; the direction of field operations on the site to be certain that plans and procedures developed are followed,
along with appropriate contract supervision; and the issuance of contracts implementing various plans and procedures developed by the consultant and approved
by reviewing agencies having jurisdiction. The primary State agencies involved
are the Departments of Environmental Conservation, Health, and Labor, along
with the Office of General Services as the lead agency. The agencies identified

�-2-

here have been provided copies of various plans for review in accordance withthe scope of their jurisdiction so that a high level of credibility is maintained,
while at the same time, maintaining a practical level of expected performance
for site operations.
After having been retained by the State, Versar Inc. embarked upon several
amjor areas of planning and research to develop proper direction for the
cleanup of the State Office Building, including the development of specific plans
for health and safety, building cleaning, solid waste disposal, air pollution
control, water treatment, building security, and research in the area of chemical
toxicity.
Because of the nature of the contaminants inside the State Office Building,
Versar developed a comprehensive Health and Safety Plan to protect both the
workers who would be entering the building and the residents of the community.
The elements of this plan include medical surveillance, protective equipment,
exposure surveillance or industrial hygiene, air pollution control, and
enforcement components. Critical sub-parts of the general programs are the
respirator program required by the Occupational Safety and Health Administration and the emergency response program. The details of the Health and Safety
Program are presented in two documents: A general Health and Safety Plan which
presents the broad outlines of the program emphasizing organization, implementation, justification, and program elements, and, as a second document, the
Health and Safety Standard Operating Procedures, which relate, in a detailed
manner, the operation of the various elements of the program.
As plans were developed, they were circulated for review and comment by
the reviewing agencies previously identified and were not finalized until the
concurrence of all parties had been achieved. Plans in final form were then
shared with the local levels of government for their information, and
presented publicly at open meetings of the Intergovernmental Coordination Group
consisting of the State agencies previously described and representatives of
Broome County government and the City of Binghamton government. Concurrently,
the plans were made available to the public by placement in the reference section
of the public libraries in the area.
The Department of Environmental Conservation has provided its expertise
concerning environmental management, primarily in the areas of the discharge of
air and water, and the management of solid waste generated by the cleanup
process. The New York State Department of Labor and the National Institute of
Occupational Safety and Health have participated in the development of our
workers' safety and health program.
Three separate contracts have been issued to implement the various areas
that have been developed and ultimately approved:
1. Air Pollution Control Systems Contract - Provided for the purchase
and installation of air pollution control equipment on the roof,
including fans, chemical and particulate filters and necessary
duct work. Material was placed on the roof by helicopter to
minimize contact with the building. Originally this equipment was
operated in a recirculating mode until test data proving the

�—3—

effectiveness of the systems was available. At that time, the
equipment was reconfigured to exhaust to the atmosphere as
originally intended.
2. Entry Module Contract - This facility was provided through the
purchase of a partially outfitted mobile structure which was
then expanded and modified to include temporary entry facilities
and locker areas, rest rooms, and security offices so that
complete control could be maintained over the workmen and other
personnel authorized to enter the building for various reasons.
All routine entry and exit from the building is through this
facility which is located on the basement level, adjacent to
the loading dock.
3. Preliminary Cleanup Contrac t - This contract is considered an
extension of the operations which were started on an emergency
basis in February and March of 1981. However, procedures have
been modified to ensure a thorough, safe, and structured approach
to this activity. This contract is not intended to produce a
building ready for occupancy, but rather is intended to accomplish
removal of soot, thereby reducing significantly the overall level
of toxicity. This operation will include high efficiency vacuum
cleaning, wiping and washing of all exposed surfaces, and many of the
readily accessible hidden areas in the building. Files, records,
personal effects and furniture will be removed and most of the
records and personal effects will be destroyed. Furniture will
be wiped down and stored in the sub-basement.
The Design and Construction Group also maintains direct control over the
entire building for contract operations and for routine building operation and
maintenance functions. The Director of field operations is the senior officer
on the site and supervises a staff of nine inspectors to oversee both contractor
work and the execution of necessary preliminary functions. Employees of the
contractor, identified in No. 3 above, are inventorying materials and equipment
within the building and collecting soot samples where untouched grossly contaminated areas can be found.
At the present time, we are awaiting a decision from the Department of
Environmental Conservation on the appropriate disposal of records and materials
described above.
Under the direction of the Design and Construction Group, the Office of
General Services has authorized Versar Inc., its consultant, to undertake a
variety of ongoing activities related to the site, the program and the overall
management of ongoing activities, as follows:
A.

PROGRAM ORGANIZATION

The Program Coordinator, a Versar employee, manages the Health and Safety
Program. As a part of his staff, a Certified Industrial Hygienist manages the

�-4-

Exposure Surveillance Program while an Occupational Physician is responsible
for the Medical Surveillance Program. In addition to their specific Program
responsibilities, the Industrial Hygienist and the Occupational Physician act
as technical consultants to the Health and Safety Officer. All on-site safety
activities are supervised by the Safety Officer.
Presently, the Safety Office is staffed on-site with 1 full-time Safety
Officer, 1 combination Safety Officer and Site Engineer, 3 Safety Technicians,
1 Respirator Technician, 2 full-time and 11 part-time Security personnel. All
of the part-time personnel are off-duty policemen from the Binghamton City
Police Department.
B.

SECURITY

The Health and Safety Office is responsible for 24-hour security of the
Building and the entry/exit facility. Two full-time security guards work
during regular working hours. They primarily regulate the movement of authorized
personnel in and out of the Building and issue proper safety clothing and gear.
Off-duty policemen maintain security during non-working hours. A close working
relationship with the Police Department ensures that all security emergencies
can be dealt with in a prompt, efficient and safe manner.
C.

CONTAMINANT CONTROL

Personnel exiting through the entry-exit facility or air backflowing from
inside to outside through the.facility could cause the movement of contaminants
from the Building. To control air flow, an air pollution control system has been
installed on top of the Building which maintains negative pressure inside the
Building. As a result, air is constrained to move from outside the entry facility
to inside the Building. In the event that the APC system shuts down, special
alarms alert in-Building personnel and a special door closes adjacent to the
entry-exit.facility to block movement of contaminants through the facility to
the outside. To ensure that workers do not inadvertently carry contaminants from
the Building they must remove all protective gear and clothing inside the Building
and shower out prior to exiting. A specially designed personnel trailer facility
containing lockers, showers and special clothes washers and dryers has been built
and connected to the Building to facilitate the movement of people in and out of
the Building. Daily smoke tests ensure that air flow in the trailer facility is
always directed into the Building.
D.

EMERGENCY RESPONSE

In the event of a fire, medical emergency or security emergency inside the
Building, complete emergency response plans have been Implemented.
E.

SUPPORT BY COMMUNITY RESOURCES

The ultimate success of any project of this scope and complexity depends
upon the close cooperation of many individuals and groups. Included in this
category are the community resources of Binghamton City and Broome County.
All emergency personnel in the community including the Fire Department, County
Health Department and the Police Department have worked closely with the Safety
Officer to ensure that the proper response will be made during any emergency.

�-5-

Medical examinations are being carried out by Our Lady of Lourdes Hospital
located in Binghamton.
F.

CONTROL OF WATER DISCHARGED FROM THE BINGHAMTON STATE OFFICE BUILDING

Temporary storage tanks have been installed in the sub-basement of the
Building to store all of the water generated during the cleanup of the Building,
including water used to clean the building, water from the clothes washers and
showers in the personnel entry facility, and water generated by condensation on
cooling coils in the air conditioning system. Water in the storage tanks is
treated by filtering through sand and activated carbon and is not released
until chemical analysis of the treated water has demonstrated that it contains
less than one microgram of PCBs per liter. Spent carbon from the treatment
system is being stored in drums for eventual disposal in a landfill approved
for disposal of high level PCB wastes.
G.

CONTROL OF AIR MOVEMENTS THROUGH THE BINGHAMTQN STATE OFFICE BUILDING

A number of modifications of the Binghamton State Office Building have been
made to control the flow through and out of the Building. The purpose of achieving
control of the air flow is to assure that the air flow through the personnel entry
trailer and through the disposal exit will be into the building, thereby preventing contamination of the personnel dressing facilities and the areas adjacent to
the Building. It was also required to prevent the dispersion of toxic materials
into the community due to movement of dusty contaminated air out of the building
at ventilation louvers, ventilating ducts, and other normal air interchange points.
Building modifications included sealing all points of possible air leaks
through the exterior of the Building, constructing personnel entry facilities
with fan forced air flow through the entry areas and into the Building, construction of an air lock to be used to remove contaminated material from the
sub-basement of the Building, and installation of two 2500 cfm exhaust fans
on the roof connected to the ventilating ducts leading to the men's and women's
restrooms on each floor. The exhaust air from the roof mounted fans is pulled
through a series of filters before being released. These filters are similar
to those commonly used to treat the air exhausted by hoods in chemical and
biological laboratories: the air is pulled through particulate filters which
are 99% effective in removing particles having a diameter of 0.3 micrometers,
and then through two activated carbon filters, each of which removes99% plus
of the volatile organic compounds from the air. The performance of the air
pollution control systems has been demonstrated through a comprehensive series
of tests performed prior to using the exhaust fans to remove air from the
Building, and the performance is continuing to be monitored by periodic tests.
In addition to the testing of the Air Pollution Control System, a number
of other air samples have been taken to determine the concentration of PCBs
in ambient air in Binghamton and to determine the concentration of PCBs in
the air inside the Building as a function of time after the exhaust fans
were turned on.

�H.

PLANNING FOR SOLID WASTE DISPOSAL FROM THE BINGHAMTON STATE OFFICE BUILDING

The loose paper and desk top items in the Building have been removed and
placed in 55-gallon steel drums for eventual disposal in a land fill approved
for disposal of PCBs. Typewriters and other office equipment have been stored
in a locked storage atea of the basement for possible decontamination. The
rest of the Building and its furnishings, including furniture, floors, ceiling
spaces, etc., is being washed with detergent and water. The contaminated
cleaning rags are being stored for eventual disposal as PCBs. A preliminary
risk assessment of the consequences of disposing of precleaned material as
non-hazardous industrial waste has been prepared and is being reviewed by the
New York State Department of Environmental Conservation.
A major study has been performed of the comparative cost of decontamination
of the Building by cleaning followed by testing to verify cleanliness vs. disposal
of most of the removable material followed by reconstruction of the building. The
cleaning option would be less expensive provided that a criteria of cleanliness is
established that is otainable and that does not result in prohibitively high
analytical costs.
I.

DISPOSAL OF CONTAMINATED DOCUMENTS IN THE BINGHAMTON STATE OFFICE BUILDING

The New York State Department of Health has advised that it is not feasible
to attempt to clean the documents that were in the Building to the point where
they can be guaranteed to be safe to handle. Various alternatives have been
considered for identifying important documents without having a large number of
people entering and working in the Building. The recommendation has been made
to destroy and bury the paper records while attempting to locate, segregate, and
save a limited number of specific items involved in litigation.
J.

COLLECTION OF SOOT SAMPLES FROM THE BINGHAMTON STATE OFFICE BUILDING

An extensive effort has been made to collect soot from horizontal
in office areas where the soot would not be contaminated by heavy dust
existing before the fire. Several hundred samples have been collected
measured areas and have been given to the New York State Department of
for use in toxicity testing and development of analytical methods.
K.

surfaces
deposits
from
Health

AIR SAMPLING IN THE GARAGE OF THE BINGHAMTON GOVERNMENT COMPLEX

Versar New York has monitored the concentration of PCBs in the air in
the publicly used County garage adjacent to the contaminated areas of the
Binghamton State Office Building. This sampling and analysis activity was
performed for the Broome County Department of Health under the sponsorship
of OGS.

DRR:sz

�NEW YORK STATE OFFICE
OF GENERAL SERVICES

DEPARTMENT

OF
HEALTH

DEPARTMENT

OF
ENVIRONMENTAL
CONSERVATION

DEPARTMENT
OF
LAIOR

SAFETY PR06RAM
COORDINATOR
(VERSAR. N.Y. INC.)

INDIVIDUALS IN
•UILDING

HEALTH AND
SAFETY OFFICE

CONTRACTOR ACTIVITIES
INSIDE BUILDING

FIGURE

1 HEALTH AND SAFETY PROGRAM ORGANIZATION

CONTRACTOR TRANSPORT
OF MATERIALS

�HEALTH AND
SAFETY COORDINATOR

CERTIFIED

SAFETY
OFFICER

INDUSTRIAL
HYGIENIST

EXPOSURE

MEDICAL
SURVEILLANCE
PROGRAM

\

SURVEILLANCE
PROGRAM

OCCUPATIONAL
PHYSICIAN

HEALTH AND
SAFETY
PROGRAM

FIGURE

2

HEALTH AND SAFETY OFFICE ORGANIZATION

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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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                <text>ambient air sampling</text>
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                <text>building remediation</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>BSOB</text>
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                <text>ambient air sampling</text>
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                <text>PCBs</text>
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                <text>building remediation</text>
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                    <text>Rom D Number

0227

°

Author
Versar New York, Inc., Springfield, Virginia

RODOrt/ArtlGlO Title Typescript: Summary Report: Measurement of Residual
Contaminants in the Air and on Surfaces in Floors 2
Through 18 of the Binghamton State Office Building
Following Completion of the Preliminary Cleanup and
Measurement of the Effect of Normal HVAC Operations
of the Concentration of Contaminants in the Air Within
and Adjacent to the Binghamton State Office Building,
August 12, 1985

Journal/Book Title
Year
Month/Day
Color
Number of Images

D

17

Descriptor! Notes

Thursday, September 20, 2001

Page 2270 of 2293

�SUMMARY REPORT:
I
MEASUREMENT OF RESIDUAL CONTAMINANTS
IN THE AIR AND ON SURFACES IN FLOORS 2 THROUGH 18 OF THE
BINGHAMTON STATE OFFICE BUILDING
FOLLOWING COMPLETION OF THE PRELIMINARY CLEANUP
AND
MEASUREMENT OF THE EFFECT OF NORMAL
HVAC OPERATIONS OF THE CONCENTRATION
OF CONTAMINANTS IN THE AIR WITHIN AND ADJACENT TO THE
BINGHAMTON STATE OFFICE BUILDING

Prepared for:
Office of General Services
State of Nev York
Albany, Nev York 12242

Prepared by:
Veraar Nev York Inc.
6850 Veraar Center
Springfield, Virginia 221S1

August 12, 1985

�1.0

INTRODUCTION

On February 5, 1981, an intense electrical fire in the basement of the
Bingharaton State Office Building (BSOB) caused coolant liquid to leak from
a transformer into the fire. This coolant liquid consisted of a mixture of
polychlorinated biphenyls (PCBs) and chlorinated benzenes. The heat of the
fire vaporized the liquid and spread black soot throughout the basement and
all 18 floors of the building. Tests of this soot performed shortly after
the fire found that it contained several percent PCBs by weight and various
polychlorinated dibenzofurans (PCOFs) at a concentration of up to several
parts per million. The analysis of the soot also identified low levels of
polychlorinated; dibenzo-p-dioxins (PCDDs) and polychlorinated biphenylenea
(PCBPs). These chemicals vere apparently created by the pyrolysis of the
PCBs and chlorinated benzenes in the transformer liquid. The Nev York
State Department of Health determined that the acute toxicity of the soot
in guinea pigs vas equivalent to a material containing 58 parts per million
2, 3, 7, 8-tetrachlorodibenzo-p-dioxin (2,3,7, 8-TCDD&gt;.
The initial cleanup of the BSOB vas halted in late February 1981 vhen
it vas learned that TCDDs were present in the work environment. The
cleaning was resumed in September 1981 after the necessary procedures and
facilities were completed to assure adequate protection of the cleanup
workers and the surrounding community during the subsequent extensive
decontamination activities. Among the precautions taken was the
sealing of existing ventilation openings and installation of an air
pollution control system on the roof of the building to clean all air that
was exhausted from the building through high efficiency particulate filters
and activated carbon.
The BSOB consists of three essentially separate ventilation zones (see
Figure 1). In September 1984, following completion of the cleaning of all
areas above the basement, the stairwells, elevator shafts, ventilating
chases, and other openings between floors 1 and 2 were sealed and the roof
mounted exhaust fans on the air pollution control equipment were connected
to a metal tube that drew air from the basement mechanical room. After
these changes were made, entry to the upper portion of the building was
possible only through the plaza level entrance on floor 2, and subsequent
cleaning has been concentrated on the basement and subbasement.
A major test plan, 'Measurement of Residual Contaminants in the Air
and on Surfaces in Floors 2 through 18....* dated September 5, 1984, was
approved by the State of Hew York C2J. This revision incorporated
suggestions made by the Expert Advisory Panel on the BSOB following reviews
of previous drafts. Three separate tests were defined with a number of
purposes:

�PENTHOUSE

w
N
O

14th FLOOR MEC.HANICAL ROOM

&gt;

N
X

UJ

m Z
3 O
O N"

6th FLOOR MECHANICAL ROOM

§1

2nd FLOOR - LOBBY

PLAZA LEVEL ENTRANCE

lit FLOOR - LOBBY, CAFETERIA

RAMP

STREET LEVEL ENTRANCE

BASEMENT - TRANSFORMER ROOM

ENTRY TRAILER

COUNTY PARKING GARAGE

SUB-BASEMENT - STORAGE

FIGURE 1. BINGHAMTON STATE OFFICE BUILDING

�First Test
1.

Determine the normal ambient levels of PCBs, PCDFs, and PCDDs in
the air in Binghamton around the BSOB.

2.

Determine whether the air in the portion of the building above
floor 1 vaa clean enough that a person could safely vork in the
upper portion of the building without wearing an air purifying
respirator, assuming that protective clothing continued to be
worn to prevent skin contact with any remaining surface
contaminants.

3.

Collect wipe samples from various surfaces within floors 2
through Id for PCB analysis to identify those surfaces which had
the highest remaining levels of residual contaminants.
I
I
I
Samples were collected from September 14 to September 17, 1984,
and the results of the analysis of the samples were summarized in the
Versar test report 'Summary of Results of the First Test...* dated January
25, 1985 C71.
Second Test
It had previously been the consensus of the Expert Advisory Panel
that the release of untreated air from the BSOB would not be
advisable until such a time that tests demonstrated that
breathing the air would not result in a significant risk to a
worker in the building. Air dispersion modeling indicated that
air released from the building due to normal operations of the
HVAC units on floors 6 and 14 would be significantly diluted, and
that any potential exposure of people outside the building to
contaminants would not be significant. The second test specified
measurements of the levels of contaminants in the air around the
building at the time normal HVAC operations were resumed as a
check on the validity of these calculations.
Third Test

1.

Teat the quality of the air in the building after several weeks
of normal operation of the HVAC system.

2.'

Measure the levels of PCDDs and PCDFs on those surfaces in floors
2 through 18 found to have the highest remaining levels of PCBs
as necessary to assess the cleanliness of the surfaces in terms
of overall toxic exposure potential.

The purpose of this summary report is to present the results of the
tests in a systematic way to facilitate a decision as to the present
cleanliness of floors 2 to 18 of the BSQB,

�2.0 AIR QUALITY AROUND THE BINGHAMTON STATE OFFICE BUILDING

Air samples vere collected on the roofs of the City Building, County
Building, and YMCA adjacent to the BSOB before normal (untreated exhaust)
ventilation was resumed using the HVAC units on floors 6 and 14 and at the
time normal HVAC operations vere started. The PCDD/PCDF air samples vere
collected using the high volume sampler developed by the Nev York State
Department of Health which uses silica gel as an adsorbent for these
contaminants, and which collects a sample of approximately 75 cubic meters.
PCB samples vere collected at the same times and locations using a
modified high volume air sampler that used urethane foam as the adsorbant
material and collects a sample of approximately 500 cubic meters of air.
The First Test air samples vere collected over a period from September
14 to 17, 1984. Duplicate PCDD/PCDF samples were collected on the roof of
the county building. The PCDD/PCDF samplers vere extracted by the NYSDOH
laboratory, which sent an aliquot of the combined extracts from the County
Building sample to Prof. Rappe at the University of Umea (Sweden) for
confirmatory analysis. Analysis of the samples by NYSDQH for PCDFs and
PCDDs did not detect any of these chemicals [61. Hovever, poor recovery
of the internal standard from the samples collected at the City Building
and the YMCA resulted in higher than expected limits of detection. Prof.
Rappe reported the possible presence of 2,3,7,8-TCDF in the aliquot of
extract from the County Building samplers, but at a level near his
detection limit and belov the detection limit achieved by NYSDOH. Since
the results obtained by Prof. Rappe vere not corrected for the recovery of
the internal standard, no accurate estimates could be made of the levels of
these contaminants that might have been present in the air.
Because of the problems vith the analysis of the ambient PCDD/PCDF air
samples from the First Test, it was decided to repeat this ambient sampling
before normal HVAC operations vere resumed. This change to the planned
test sequence was documented in the Test Plan Modification dated February
14, 1985 C83. This Test Plan Modification also reflected the decision of
the Nev York State Department of Health Laboratories to analyze the air
samples only for tetra and penta CDFs in an attempt to achieve the
detection limit at which Prof. Rappe reported the possible presence of
2,3,7,8-TCDF in the ambient air sample from the First Test. In accordance
vith this Test Plan Modification, duplicate PCDD/PCDF air samples and PCB
samples vere collected on the roofs of the City Building, the County
Building, and the YMCA on February 15 - 18, 1985. Duplicate PCDD/PCDF air
samples and PCB samples vere again collected on February 22 - 25, starting
vhen the HVAC units on floors 6 and 14 vere returned to normal operating
conditions, releasing untreated air from louvers on these floors.
The results of the analysis of the ambient air samples for PCBs vere
reported in a Test Report dated May 17, 1985 [121. The quantities of PCB1254 (the type of PCB released in the BSOB) found in the ambient air at the
three tested locations vere as summarized in Table 1.

�TABLE 1

PCBa in Ambient Air (micrograms per cubic meter) Before and After
Normal HVAC Operations Started in the BSOB on February 22, 1985.
Location

September
14-17, 1984

February
15-18,1985

February
22-25,1985

YNCA

003
.0

001
.02

&lt;0.0003

County Bldg.
City Bldg.

002
.0
0.002

0.0012
0.0013

000
.09
&lt;O.OQ03

The results of the analysis of the six February ambient,air samples
for tetra and penta CDFs vere reported by HYSDOH in their report dated
July 17, 1985 Cl71. Ho 2,3,7,8-TCDF vas detected in any of the samples at a
maximum detection limit of 0.15 picograms per cubic meter. Ho 2,3,4,7, 8penta CDF or 1,2,3,4,8-penta CDF vas detected at a maximum detection limit
of 0.5 picograms per cubic meter. Prof. Rappe verbally reported that his
laboratory did not identify the presence of toxic contaminants at a
detection limit of one picogram per cubic meter C163.
The analysis of samples of ambient air taken before normal HVAC
operations vere started and immediately after the HVAC systems on floors 6
and 14 vere returned to normal operating conditions indicates that the
release of untreated air from the- Binghamton State Office Building did not
result in measurable or significant contamination of the air around the
BSOB.
3.0 AIR QUALITY IH FLOORS 2 THROUGH 18

In accordance vith recommendations from the Expert Advisory Panel on
the Binghamton State Office Building, release of untreated air from the
BSOB vould be advisable only after the quality of the air in the building
vas demonstrated to sufficiently clean that it vould be safe for
reconstruction vorkers to breath the air in the building. It vas the
consensus of the Panel that a dioxin equivalent level of not more than 14
picograms per cubic meter in the air in the building vould be required
before entry vithout respirators vould be advisable, assuming that
precautions continued to be taken to prevent skin contamination.
The Test Plan specified that air samples vould be collected for PCBs
and PCDDs/PCDFs in the building during the First Test to determine vhether
the air vas sufficiently clean that vorkers could enter the building
vithout respirators. PCDD/PCDF and PCB air samples vere collected in the
return air plenums of the mechanical rooms on floors 6 and 14. The air
entering these plenums returns from all of the areas served by each of the
HVAC systems, and so measurements taken at these locations are a good

�indication of the average air vithin each HVAC zone. The PCOD/PCDF air
samples vere collected over a period of 64 hours. Three PCB samples vere
collected at each location during this period, each PCB sample being
collected over a period of about 21 hours. In addition, PCB air samples
vere taken adjacent to the barriers between floors 1 and 2 to check on the
adequacy of the partitions in preventing a spread of contamination from the
lover to the upper portions of the building.
The results of the analysis of PCB air samples vere summarized in the
Versar report dated January 25, 1985 [71. The maximum_PCB concentration in
the air in the dead air spaces in the elevator shaft and stairwell betveen
floors 1 and 2 on clean side of the partition vas 1 microgram per cubic
meter. The PCB levels in the air passing through the HVAC units on floors
6 and 14 ranged from 0.2 to 0.9 micrograms per cubic meter (average » 0.32
on floor 6 and 0.7 on floor 14).
The results of the analysis of the PCDD/PCDF air samples by NYSDOH and
Prof. Rappe vere summarized in an undated NYSDOH report CS1. The report
calculated the average dioxin equivalent air quality based on measured
tetra, penta, and hexa CDFs and 2, 3,6,7-TCBP to be 8.5 picograms per cubic
meter, and concluded that the average air quality vould be belov 11
picograms per cubic meter even if all of the non-detected dioxins and
penta-CBPs vere present at the detection limits achieved in these tests.
Based on these results, the Office of General Services submitted to
the Nev York State Department of Environmental Conservation a formal Hotice
of Determination of Non-significance for the planned resumption of normal
operations of the HVAC systems, vith the resultant release of untreated air
from the BSOB [93. This action vas taken on February 22, 1985.
The Test Plan for the Third Test sampling to determine the quality of
the air in the BSOB after the resumption of normal HVAC operations vas
modified on March 29, 1985, to add 63 PCB air samples from throughout the
building to check on the relative homogeneity of the air vhile PCB and
PCDD/PCDF air samples vere being collected -in the return air plenums of the
HVAC mechanical rooms on floors 6 and 14 C101. These air samples vere
collected over the period March 29 - April 1, 1985. The results of the PCB
analysis of these samples is presented in Table 2. The only measurable
levels of PCBs at a detection limit of about 0.16 ug/m* vere in the men's
restrooms. After the building is renovated, air vill be constantly
exhausted from the restrooms by a separate exhaust system in order to
control odors. This vill reduce the levels of PCBs in the air.
The results of the analysis of these samples for CDFs vas reported by
NYSDQH in their report dated July 17, 1985 C43. The samples from the HVAC
air return plenums contained measurable amounts of 2,3,7,8-TCDF and
2,3,7,8,X-Penta CDFs, but no hexa CDFs, PCDDs, or PCBPs. The NYSDOH
calculated the dioxin equivalent concentration in the air in the building
five veeks after normal HVAC operations vere started to be &lt;4.1 picograms
per cubic meter vs &lt;11 picograms per cubic meter in November, 1984.

�TABLE 2
PCB ANALYSIS OF AIR SAMPLES COLLECTED IN THE BSOB
MARCH 29 - APRIL 1, 1985

Floor
2
2
2
2
2
2
2
2
2

Location
Elevator Lobby
NE Floor 2 fl
NE Floor 2 #2
NE Floor 2 #3
West stairwell
West elevator shaft
East elevator shaft
Men's room
' East stairwell

PCBs ug/mj.
NO
ND
ND
ND
HD
ND
0.34
ND
ND

3
3
3

Elevator lobby
Women's room
Northeast corner

ND
ND
ND

4
4
4

Elevator lobby
Men's room
Northeast corner

ND
0.43
ND

5
5
5

Elevator lobby
Women's room
Northeast corner

ND
ND
ND

6
6

Elevator lobby
Men's room

6

Northeast corner

ND
0.31
ND

7
7
7

Elevator lobby
Women's room
Northeast corner

ND
ND
ND

8
8
8

Elevator lobby
Hen's room
Northeast corner

ND
ND
ND

9
9
9

Elevator lobby
Women's room
Northeast corner

ND
ND
ND

10
10
10
10
10

Elevator lobby
Men's room
East Stairwell
West Stairwell
Northeast corner

ND
ND
HD
ND
ND

�11
11
11

Elevator lobby
Women's roan
Northeast corner

NO
NO
HD

12
12
12

Elevator lobby
Hen's roo»
Northeast corner

NO
HD
NO

13
13
13

Elevator lobby
Women's room
Northeast corner

ND
ND
ND

14
14
14

Elevator lobby
Hen's room
Northeast corner

ND
0.37
ND

15
15
15

Elevator lobby
Women's room
Northeast corner

ND
ND
ND

16
16
16

Elevator lobby
Hen's room
Northeast corner

ND
ND
ND

17
17
17

Elevator lobby
Women's room
Northeast corner

ND
ND
ND

18
18
18
18
18
18
18

Elevator lobby
Hen's room
East atairvell
West stairwell
Northeast corner tl
Northeast corner #2
Northeast corner #3

ND
0.37
ND
ND
ND
ND
ND

14
14
14

HVAC
HVAC
HVAC

#A-8
fA-9
fA-10

ND
ND
ND

6
6
6
6
6
6

HVAC
HVAC
HVAC
HVAC
HVAC
HVAC

fA-1
#A-2
fA-3
*A-4
fA-5
*A-6

ND
ND
ND
ND
HD
HD

.

i

|

.

ND: None detected at detection limit of 0.2 ug/tube,
approximately 0.16 ug/m*.

8

�4.0 CLEANLINESS OF SURFACES ON FLOORS 2 THROUGH IS

First Teat
The first teat collected 48 vipe samples that vere analyzed for PCBs
In order to identify those surfaces that might have the highest levels of
residual PCDDs and PCDFs. Wipe samples vere also collected from Id of the
locations for analysis for PCDDs and PCDFs by Battelle. The purpose of
these samples vas to establish the ratio of PCBs to total •dioxin
equivalent' toxicity so as to determine vhether PCB levels could be used to
identify locations having elevated levels of PCDDs and PCDFs. Tvo
duplicate vipe samples vere also analyzed for tetra through hexa CDFs by
the NYSDOH laboratory.
the results of'all of these analyses vere reported in a formal test
report 171. The average value of all 48 vipe samples vas 16.6 ug/m*. Wipe
samples have been collected by HIOSH from a number of buildings vhich have
not had knovn sources of PCBs, and the levels that have been found have
usually averaged about 10 ug/m* vith occasional samples as high as 50 ug/m*
not being unusual til. Only three vipe samples from the BSQB vere found to
have levels above SO ug/m*. These samples vere collected from the top of a
ceiling light fixture in the 17th floor elevator lobby vhere the plaster
ceiling made access difficult (100 ug/m*), a stair tread in the east
stairvell betveen floors 17 and 18 (120 ug/m* &gt;, and a sample from the floor
in the 17th floor elevator lobby (150 ug/m*). Since it vas reasonable that
these elevated levels vere an indication of possible quality control
problems vith the cleaning of the ceiling light fixtures and stair treads,
all of the light fixtures in the core area of floors 2 through 18 vere
subsequently recleaned, and the stair treads in both stairvells vere also
recleaned. The floor sample from the 17th floor elevator lobby vas from a
deposit of mastic that remained on floors throughout the building after the
vinyl tile vas removed. This tile vill be replaced before the building is
occupied, and the mastic vill therefore not be accessible to skin contact.
A test application of nev tile has been installed in the building, and is
being tested periodically to determine vhether the measured PCB levels
increase vith time due to PCBs penetrating through the tile.
An analysis of the eighteen samples for PCDDs and PCDFs by Battelle
found that the levels of PCDDs vere generally lov to undetected, vith all
2,3,7,8-TCDD levels at or belov one nanogram per square meter. The
calculated contamination levels for the 18 PCDD/PCDF vipe samples in terms
of "dioxin equivalents' ranged from .01 to 81.7 ng/m*, the highest levels
being found in the samples collected from the ceiling lighting fixtures in
the core (81.7 ng/m*), and from the stair treads betveen floors 17 and 18
(31 ng/m*) and betveen floors 7 and 3 (30.1 ng/m*). The only other
significant level vas found in the sample taken from the coated surface of
the men's room exhaust chase on floor 17 (16.6 ng/m*) [41. The surface of
this chase vas subsequently painted vith epoxy paint. The tetra and penta
CDFs contributed 95X to 98% of the calculated dioxin equivalent levels.

�A linear regression analysis of the log transformed PCB and dioxin
equivalent data found a correlation coefficient of 0.77. If this
relationship were used to predict the expected dioxin equivalent levels
from the measured PCB levels, the predicted dioxin equivalent levels vould
be within an order of magnitude (from 0.1 to lOx) of the measured levels
92% of the time [53.
Third Test
Based on information obtained from the First Test samples and
suggestions made by members of the Expert Advisory Panel following a review
of these results, certain changes vere made to the test plan for the Third
Test as documented in the Test Plan Modification - Third Test dated March
29, 1985 C101. These changes specified that the vipe sampling vas to be
conducted in tvo phases: the first phase vas to collect 35 wipe samples
from types of surfaces found to have high levels of PCBs during the First
Test that were subsequently recleaned and from surfaces not previously
tested such as the stone floor and walls in the second floor plaza lobby.
Aliquots of the extract from eleven of the samples were also to be analyzed
by Battelle for PCBs as a check on the analytical methodology. Following
analysis of the 85 samples for PCBs, the 10 locations found to have the
highest PCB levels were to be wipe sampled to determine the levels of !
PCDFa.
The 85 PCB wipe samples specified in the amended test plan and the
eleven samples for duplicate analyses were collected on March 29, along
with 5 additional samples from areas selected by Mat Gillen who observing
the sampling on behalf of the Public Employees Federation. The results of
the PCB analysis of all 101 wipe samples were included in the Test Plan
Amendment dated May 28 which covered the collection of wipe samples for
PCDF analysis C13, attachment A]. The average PCB level of these 101
samples was 7.8 micrograms per square meter. The results of the duplicate
analysis of 11 samples by both Versar and Battelle were not significantly
different (correlation coefficient = 0.997) CIS].
Only two PCB wipe samples were above 50 ug/m*: stair tread from west
stairwell on floor 2, 110 ug/m* as measured by Versar, 106 as measured by
Battelle; stone floor from floor 2 plaza lobby, 62 ug/m* measured by
Versar, 74 ug/m* measured by Battelle. However, eight of the 10 highest
measurements were from stair treads and landings in the stairwells. In
order to provide additional assurance as to the cleanliness of the
building, 06S had the stairwell treads and landings and the stone floor on
floor 2 recleaned, and had the stair treads painted with epoxy paint. (The
stair landings, like most of the floors in the building, will be eventually
covered by new vinyl tile.) These surfaces were retested for PCBs as
specified in the Test Plan Modification dated May 3, 1985 [111. Thirteen
wipe samples were collected from landings and stair treads on May 5, and
the results from this retest were also included in the May 28 Test Plan
10

�Amendment C13, attachment Bl.
4 ug/m*.

None of these samples shoved PCS levels above

Based on the results of the March 29 sampling and the Hay 3 resampling
of recleaned stairways, it was possible to select surfaces for PCDF
sampling which met the criteria of representing the 10 highest PCB levels
without having all of the samples being taken in the stairwells. The
wipe sampling for PCDFs was defined in the Hay 28 Test Plan Amendment C13],
which included 11 locations selected by OGS and an additional 6 locations
suggested by Dr. Terry Killer. All samples were to be analyzed by
Battelle, for tetra and total penta dibenzofurans, and aliquots of the
extract from two wipe samples were to be sent to the Mew York State
Department of Health Laboratory for confirmatory analysis. PCB wipe
samples from the same locations were analyzed for PCBs by Versar. These
samples were collected on Hay 28, and the results of the Battelle analyses
were summarized in the Battelle Final Report dated July 19, 1985 [ 8 .
1]
The PCDF results, the PCB measurements, and the calculated dioxin
equivalent contamination levels based on the levels of 2,3,7, S-TCDF and
total penta-CDFs are summarized in Table 3. The highest dioxin equivalent
levels were found on the top of ceiling light fixtures from floors 12 and
16 (12.6 and 14 ng/m*), from the concrete floor in the elevator lobby on
floor 7 (12.5 ng/m*), and from the stone floor on floor 2 (13.8 and 12.8
ng/m*). The First Test wipe samples, which were analyzed for tetra through
hexa CDDs and CDFs, showed that 95X to 98X of the dioxin equivalent level
was the result of the presence of tetra and penta CDFs. Assuming that
PCBPs might contribute an additional 10% to the toxicity, the contaminant
levels calculated from the Test Three data may underestimate the total
surface contamination by up to 15%, so the maximum contaminant level might
actually be 16.4 ng/m* rather than 14 ng/m*.
The two samples that were also analyzed by the Hew York State
Department of Health Laboratories were from the stone floor in the floor 2
lobby and from the vinyl wall in the elevator lobby on floor 12. The
comparable analytical data from the two laboratories are summarized in
Table 4. A linear regression analysis of the log transformed PCB and
dioxin equivalent data is shown in Figure 2. The NYSDOH analysis was
performed using low resolution mass spectrometry, but did quantify the
specific isomers of penta-CDFs that were chlorinated at the 2, 3, 7, and 8
positions. Both laboratories found about the same levels of 2,3,7,8-TCDF.
Although HYSDQH found higher levels of total penta CDFs in both samples,
the percentage of the penta-CDFa that was chlorinated at the 2, 3, 7, and 8
positions was significantly lower that* the assumed SOX used to calculate
the dioxin equivalents from the Battelle data, so the final calculated
dioxin equivalent levels were essentially identical for the two
laboratories.

11

\

�TflBLE 3
RNflLYTICflL RESULTS FOR PCBS RNO OIOXIN EQUIVALENTS FOR WIPE SAMPLES COLLECTED MAY 29, 1985 IN THE BSOB

ng/«2

SAMPLE
2378
,,,TCDF

2791
29
74
2795
29
76
29
77
20
60
2801
20
82
2810
29/
723
29/0
723
29/
789
20
86
20
84
2803
20
88
20
89
20
85
2807
2813
2811

TOTAL
PENTACOFs

37
.0
77
.0
13.00
12.00
- 18.70
44
.0
1.70
1.20
03
.0
15.50
11.90
1.00
09
.0
2.50
00
.0
24
.0
07
.0
28
.0
1.10
06
.0
04
.0

11.90
2.0
23
5.0
78
51.70
* 3ft
7

38
.0
4.10
26
.0
00
.0
51.50
5.0
30
1.50
1.00
00
.0
1.40
2.30
00
.0
00
.0
1.90
00
.0
00
.0

ug/oi2
OIOXIN
EQUIV

3.22
62
.8
13.97
12.62
12*45__
2.10
1.25
08
.3
0.10
13.75
12.80
05
.8
04
.7
08
.3
0.23
1.18
02
.3
09
.3
06
.8
02
.0
0.13

PCBs

23
4
5
5
31
16
8
&lt;0.5
&lt;0.5
26

6
2
2
2
4
2
2
&lt;0.5
&lt;0.5
&lt;0.5

STAIR TREAD, FLOOR 2; WEST STAIR WELL
STAIR NOSING, FLOOR 18
CEILING LIGHT, FLOOR 16 NE
CEILING LIGHT, FLOOR 10 CORE
CONCRETE FLOOR, FLOOR 7 CORE
INSIDE OF MEN'S ROOM DOOR, FLOOR 3
VINYL WALL, FLOOR 9 CORE
INSIDE WOMEN'S ROOM DOOR, FLOOR 15
FIELD BLANK
STONE FLOOR, FLOOR 2 CORE
DUPLICATE ANALYSIS 2792/3
VINYL WALL, FLOOR 16 CORE
STAIRWAY LANDING, FLOOR 12 WEST STAIRWELL
STAIR TREAD, FLOOR 14 EAST STAIRWELL
COLUMN ENCLOSURE, FLOOR 6 NE PERIMETER
STAIRWAY LANDING, FLOOR 8 EAST STAIRWELL
STAIRWAY LANDING, FLOOR 5 WEST STAIRWELL
STAIR TREAD, FLOOR 13 EAST STAIRWELL
STAIR TREAD, FLOOR 11 WEST STAIRWELL
LABORATORY BLANK
FIELD BLANK

�TABLE 4

Comparison of Battelle and NYSDQH analysis of PCDF wipe samples
Isomer or Class
Vinvl Wall Sample
2,3,7,8-TCDF
Total TCDFs
1,2,3,7,8-Penta CDF
Total Penta CDFs
Stone Floor Sample
2, 3, 7, 8-TCDF
Total TCDFa
1,2,3,7,8-Penta CDF
Total Penta CDFs

5.

HYSDOH

Battelle
,\fof

0.9
5.7
0.38
1.3
17.
9.
8
18.8
9.
5

ng/m«
ng/m*
ng/m*
ng/m*
ng/ra*
ng/m*
ng/ra*
ng/m*

1.0
8.0
0.39
1.5

ng/m*
ng/m*
ng/m*
ng/m*

A//5

15.5 ng/m*
63. ng/m*
16.3 ng/m*
ng/m*
52.

CONCLUSIONS

The release of untreated air from the Binghamton State Office Building
when the HVAC units on floors 6 and 14 were returned to normal operating
conditions did not cause any measurable contamination of the ambient air
around the building. The initial contamination level of the air being
vented from the building was &lt;11 picograms dioxin equivalents per cubic
meter.
The air in floors 2 through 18 of the BSOB on April 1 (five weeks
after the HVAC units started normal operations) contained &lt;4.1 picograms
dioxin equivalents per cubic meter. The air in floors two through 18 did
not contain measurable levels of PC8s at a detection limit of about 0.16
ug/mj, except in one elevator shaft and in the men's restrooms where the
levels of PCBs were up to 0.43 ug/m*.
Surfaces in the BSOB in late Hay generally had contamination levels of
less than one nanogram dioxin equivalents per square meter except for the
tops of ceiling lighting fixtures, the concrete floor on floor 7, and the
stone floor on the floor 2 plaza entry. The maximum levels of dioxin
equivalent contamination calculated from measurements of 2,3,7,8-TCDF and
total penta-CDFs did not exceed 14 nanograms per square meter on any of the
samples. Adjusting for the possible presence and contribution of PCDDs,
hexa-CDFs, and PCBPs, the total dioxin equivalent contaminant level of the
highest sample might have been as high as 16.4 nanograms per square meter.

13

�FIGURE 2

RATIO EVALUATION BSOB WIPES

or

w

o
»-»

n
CJ

3

1.2
1.1 1 0.0 O.B 0.7 0.6
0.5 0.40.3 0.2 0.1 0
-0.1 - D
-0.2 - D
-0.3 -0.4 -0.5 -0.6 -0.7
I
I
-0.7
-0.5

only furan analysis performed
P
a

a
D

D
D

D

D
T

i i
r i i i
i
i
i i i i i T i f \ i
-0.3 -0.1
0.1
0.3
0.5
0.7
0.0
1.1
1.3
1.5
D

LOG PCB
MAY 20,1085

�REFERENCES

Cll

Korainaky, J.R.; J.M. Melius; J.PFlesch. (MIQSH Cincinnati).
Assessing PCB Contamination from Electrical Equipment Failures. Paper
presented at the American Industrial Hygiene Conference, Philadelphia,
Pa. Hay 22-27, 1983.

C2J

Test Plan: Measurement of Residual Contaminants in the Air and on
Surfaces in Floors 2 through Id of the Binghamton State Office
Building Following Completion of the Preliminary Cleanup and
Measurement of the Effect of Normal HVAC Operations on the
Concentration of Contaminants in the Air Within and Adjacent to the
Binghamton State Office Building. September 5, 1984.

C31

DeRoos, Fred. L. (Battelle Columbus Laboratories). Untitled letter
report dated October 26, 1984 to Or. Richard Ronan, Versar Inc. t
(Included in C2] as Appendix E)

C41

Westin, R.A. (Versar Nev York Inc.) Versar and Battelle Analytical
Results from First Test, September 5 Test Plan. Letter to H. Stevens
dated November 20, 1 8 .
94

C5] Westin, R.A. (Versar Nev York Inc.) Toxic ratio PCBs/TCDD
equivalents in vipe samples from First Test. Letter to H. Stevens
dated November 28, 1984.

'

C6] Aldous, K.; D. Bilker; P. O'Keefe; R. Smith; 6. Eadon. Chemical Data
on Air and Wipe Samples Collected from the Binghamton State Office
Building - September 1984. Nev York State Department of Health.
Undated. (Included in £23 as Appendix D)
C7] Test Report: Summary of Results of the First Test To Determine
Residual Contaminants in the Air and on Surfaces in Floors 2 through
18 of the Binghamton State Office Building. Versar Nev York Inc.
January 25, 1985.
C81 Test Plan - Modification. Second Test: Measurement of the Effect of
Normal HVAC Operations on the Concentration of Contaminants in the Air
Within and Adjacent to the Binghamton State Office Building. Versar
Nev York. February 14, 1985.
[9] Egon, J. (Nev York State Office of General Services.) SEQR Negative
Declaration: Notice of Determination of Non-Significance: Return to
Normal HVAC Operation of Floors 2 to 18 of the Binghamton State Office
Building (BSOB). February 20, 1985.
CIO] Test Plan - Modification. Third Test: Measurement of the Levels of
Toxic Chemicals Remaining in the Air and on Surfaces in the Binghamton
State Office Building Following Resumption of Normal HVAC Operations.
Versar Nev York Inc. March 29, 1985.

�[Ill Test Plan - Modification, Third Test Addendum: Measurement of the
Levels of Toxic Chemicals Remaining on Surfaces in the Stairwells in
the Binghamton State Office Building. Versar Nev York Inc. May 3,
1965.
[12] Test Report - Summary of Results of the Second Test to Determine
Ambient Air Concentrations Prior to Venting and During Venting Around
Binghamton State Office Building - PCB Measurements. Versar Nev York
Inc. May 17, 1985.
[13] Test Plan - Amendment to Modification of Third Test Dated March 29,
1985: Measurement of the Levels of Toxic Chemicals Remaining in the
Air and on Surfaces in the Binghamton State Office Building Following
Resumption of Normal HVAC Operations, Versar New York Inc. May 28,
1985.
'
'
*
C141 Sampling Report. Amendment to Third Test of the Cleanliness of Floors
2 - 18 of the BSOB: May 28, 1985. Versar New York Inc. June 11,
1985.
[153 Hestin, R.A. (Versar Nev York Inc.) PCB results from analyses of
split extracts by Battelle and Versar. Letter to H. Stevens dated
June 18, 1985.
[16] Eadon, G. (Nev York State Department of Health.) Split Sampling
Results - BSOB Outdoor Air. Memo dated July 11, 1985.
[17] Smith, R.; P. O'Keefe; X. Aldous; D. Milker; G. Eadon. (Nev York State
Department of Health.) Chemical Data on Air Samples Collected in and
Near the Binghamton State Office Building (February, March 1985)
Before and After the HVAC is Returned to Normal. July 17, 1985.
[18] DeRoos, F.L.; S.C. Watson. (Battelle Columbus Laboratories.) Final
Report on Measurement of Polychlorinated Dibenzofuran Levels in
Surface Wipes from the Binghamton State Office Building. July 19,
1985.

16

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02268

Author

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KOpOPt/ArtlClB TltlO Memorandum: State of New York Expert Panel
Meeting, 12-13 August 1985, from Alvin L. Young to
Bernadine Healy, August 1,1985

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Young requests approval to participate in meeting.
Attachment missing.

Thursday, September 20, 2001

Page 2268 of 2293

�EXECUTIVE OFFICE OF THE PRESIDENT
OFFICE OF SCIENCE AND TECHNOLOGY POLICY
WASHINGTON, D.C. 20506

August 1, 1985

MEMORANDUM FOR BERNADINE HEALY
FROM:

AL

SUBJECT:

State of New York Expert Panel Meeting
12-13 August 1985

As discussed with you on 31 July, I have received a letter
(attached) from the Department of Health, State of New York,
announcing a meeting for August 12-13 of the Expert Panel for
the Binghamton State Office Building PCB/Dioxin Episode.
In February 1981, a large electrical transformer fire occurred
in the 18-story State Office Building in Binghamton, New York.
The intense fire released large quantities of PCBs, dibenzofurans,
and dioxins. The State of New York formed an Expert Panel to
assist in developing recommendations and in monitoring the
clean-up program. I have served on the Panel since its first
meeting in April 1981. The meting in Binghamton on August 12-13
should conclude the program. The State of New York will cover
all expenses. I solicit your approval for my participation.
Proposed Schedule
Depart Washington National, August 12, 9:05 a.m.
Return Washington National, August 13, 5:30 p.m.
Accomodation for August 13
Best West Hotel DeVille
Binghamton, New York
Approve

607-722-7272

Disapprove

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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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