United States
 Environmental Protection
 Agency
Environmental Monitoring Systems
Laboratory
Research Triangle Park NC 27711
 Research and Development
EPA/600/S4-85/044  Aug.
 Project  Summary
Ambient  Monitoring for
PCB Near Three  Landfills in the
Bloomington,  Indiana  Area
 D. L. Sgontz and J. E. Howes, Jr.
  A monitoring program was conducted
 to determine PCB levels in ambient air
 on and in the vicinity of three landfills in
 the Bloomington, Indiana area. Fixed-
 height measurements were made at
 locations on the sites where capacitors
 containing PCB were exposed and at
 nominally upwind and downwind loca-
 tions. Vertical PCB  concentration pro-
 files were also obtained at five elevations
 above selected hot spots. Sampling was
 performed over 8-hour daytime periods
 (approximately 0900-1700 hours) and
 over 24-hour periods at various on- and
 off-site locations. Polyurethane foam
 (PUF) cartridges  used either with
 DuPont personal-type sampling pumps
 or EPA-developed high volume samplers
 were used for collection of PCB from
 the ambient air. At  Neal's  Landfill,
 airborne PCB concentrations measured
 180 cm above five hot spots during 8-
 hour daytime sampling periods, ranged
 from 0.4 to 18  /ug/scm. PCB  levels
 observed along the downwind perimeter
 of the site  ranged  from 0.2 to 1.8
 /ug/scm. Upwind PCB concentrations
 measured during the 4-day monitoring
 period ranged  from  <0.05 to 0.1
/ug/scm. Ambient air  PCB  concentra-
tions measured at 180 cm above two
 hot spots on Neal's Dump during 8-
 hour daytime periods ranged from 0.6
to 19 yug/scm. Over  the 3-day monitor-
ing period, PCB levels determined near
residences adjacent  to the site ranged
from <0.04 to 0.2 /ug/scm. At Lemon
Lane  Landfill, ambient air PCB levels
measured at 180 cm above three hot
spots during 8-hour daytime sampling
periods ranged from 6 to 193 /ug/scm.
Over the 4-day monitoring period, up-
wind airborne PCB concentrations were
fairly constant at approximately 0.05
yug/scm and levels measured downwind
of the landfill; ranged from 0.3 to 0.8
fjg/scm. Generally, the airborne PCB
levels measured at hot spots on the
landfills appear to be correlated with
the quantity of exposed capacitors, i.e..
those visible at or above ground level.
PCB emission rates and thus airborne
levels were probably maximized by the
unseasonably warm, dry weather which
prevailed throughout  the field  study
period.
  This Project Summary was developed
by EPA's Environmental Monitoring
Systems Laboratory. Research Triangle
Park, NC, to announce key findings of
the research project that is fully docu-
mented in a separate report of the same
title (see Project Report ordering in-
formation at back).

Introduction

  Three landfills in the  Bloomington,
Indiana, area have been used for disposal
of capacitors containing polychlorinated
biphenyls (PCBs). The landfill sites are
identified as: Neal's Landfill, Neal's Dump,
and Lemon Lane Landfill. Visual surveys
of these sites have indicated several areas
where capacitors are visible at or above
ground level. In most  of these areas,
leakage of the  capacitors is suspected
due  to apparent wetting of the soil and
damage to the surrounding vegetation.
As a consequence of the leakage, PCBs
may be emitted, thus  creating  an air
pollution problem.

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   During June and July 1983, a field
rpr»gram was conducted to monitor PCB
 levels  in  the ambient air  at  selected
 locations on and surrounding the three
 landfill  areas. Airborne PCB measure-
 ments on the sites were performed at
 localized areas (hot spots) where leaking
 capacitors were evident. Measurements
 were made at locations in the vicinity of
 the sites to determine upwind background
 levels  and downwind  emission levels.
 Three types of samples were obtained
 during the study to measure ambient air
 concentrations and emission patterns.
 All sampling was performed with systems
 which employed polyurethane foam (PDF)
 cartridges for collection of PCBs from the
 ambient air.  (a) Battery-operated, per-
 sonal-type pumps were used to sample
 during 8-hour daytime periods at a fixed
 height above  hot spots and at  upwind
 locations,  (b) EPA high-volume systems
 were used to sample for 8- and 24-hour
 periods at hot spots  and  upwind and
 downwind points, (c) Arrays  of five
 battery-operated sampling systems oper-
 ated at different heights above ground
 level were used to determine the vertical
 concentration profiles at hot spot areas
 during 8-hour daytime periods. The quan-
 tity of PCBs collected in the PDF cartridges
 during sampling was determined by ex-
 traction and  analysis  of the extract by
 electron-capture  gas chromatography
 using EPA Method 608. Meteorological
 conditions (wind  speed and direction,
 temperature, and relative humidity) were
 monitored during sampling at the sites to
 assist in interpretation of the PCB meas-
 urements.
   This study was conducted to provide
 EPA Region V with data on background
 airborne levels and the magnitude  and
 distribution  of PCB emissions into the
 atmosphere on and around the three
 landfill  areas. EPA Region V  will  use
 results to assess the impact of the PCB
 emissions from the landfills on the public
 welfare and to determine  the  need for
 remedial action to reduce the emissions
 into the environment.


 Experimental

 Sampling Procedures
   Three different sampling procedures,
 i.e., (a) low-volume, (b) vertical profile,
 and (c) high-volume were used to measure
 ambient air   PCB  concentrations  and
 emission patterns on and in the vicinity of
 the landfill sites.
   DuPont P-4000A battery-operated, low
 volume samplers (flow rate ~3.8 L/min)
were used to sample the ambient air at
hot spots  on  the landfill sites and at
upwind  locations. The  samplers were
positioned with inlets of the PUF cart-
ridges  at  1.8  m  above ground level.
Sampling at hots spots was performed
immediately downwind  of the hot  spot
area over 8-hr daytime periods from
approximately 0900 to 1700 hrs CDT.
  Measurements  of the vertical  PCB
concentration  profiles were performed
with a vertical array of five DuPont low
volume  samplers. The array was posi-
tioned directly over a hot spot area with
inlets of the PUF cartridges at 2, 30, 60,
120, and 180 cm above ground level.
Sampling was performed for 8-hr periods
from approximately 0900 to 1700 hrs
CDT.
  EPA high volume systems (flow rate ~8
cfm) were used to collect 8-  or 24-hr
samples upwind of the sites, at hot spots
on the sites,  and along the downwind
perimeter of the sites. The EPA samplers
were situated  with the inlets approxi-
mately 1.2 m  above ground level  and
were located,  to the extent possible, in
areas where air flow was unrestricted in
the windward  direction.
  At hot spots, the high volume samplers
were positioned immediately downwind
of the hot spot area. Eight-hour samples
were collected concurrently with the low
volume  samples, i.e., during  sampling
periods from approximately 0900 to 1700
CDT. The 24-hr samples were collected
from approximately 0800 hr  to 0800 hr
the following day.

Analysis Procedures
  Analysis for PCBs in the PUF cartridges
(and high volume filters) was performed
according to the procedure described in
the EPA Manual of Analytical  Methods.
The steps  in the  analysis  procedure
included: (a) Soxhlet  extraction  of the
foam plugs (and filters in the case of  high
volume samplers) with 5 percent ether in
hexane; (b) concentration of the extract to
1 mL and; (c) determination of PCBs in an
aliquot of the extract by electron capture-
gas chromatography using EPA Method
608. These analyses were performed by
Southwest Research Institute.

Meteorological Measurements
  Continuous  measurements of wind
speed, wind direction, and ambient tem-
perature were performed with  Meteoro-
logical  Research,  Inc.  (MRI) portable
weather stations. One unit was located at
Neal's Landfill during the entire study. A
second unit was used to collect meteoro-
logical data at Neal's Dump and Lemon
Lane Landfill during the PCB monitoring
periods at these sites. Strip chart data
from the meteorological systems were
manually reduced to obtain hourly aver-
ages. Relative humidity data were obtain-
ed from wet- and dry-bulb temperature
measurements made periodically during
daytime sampling periods.


Results and Discussion
  The monitoring results from the low
volume  sampling show  that PCBs are
being introduced into the atmosphere
from leaking capacitors  at each of the
three landfills.  Generally,  the  airborne
levels measured at hot spots on the sites
appear to correlate with the number of
exposed, leaking capacitors. The highest
PCB concentrations in ambient air were
found on Lemon Lane Landfill. At This
site, levels  measured in three different
areas with exposed capacitors  during 8-
hour daytime periods ranged from 6 to
193 jug/scm. The highest values (40 to
193 jug/scm) were observed immediately
above the large bank of exposed capaci-
tors along the south end of the site. PCB
levels measured by low volume sampling
at the five  hot  spots on Neal's Landfill
during 8-hour daytime periods ranged
from 0.4 to 20 //g/scm. At Neal's Dump,
PCB concentrations detected at two hot
spots during 8-hour daytime monitoring
with low volume samplers ranged from
0.6 to 19 fjg/scm.
  PCB emissions from leaking capacitors
were also detected in the ambient  air
downwind  from the landfill areas.  At
Neal's Landfill, PCB  concentrations
measured at four downwind  locations
ranged from 0.2 to 1.8 //g/scm with the
highest  values  being observed at the
locations closest (—12-30  m) and  most
directly downwind of the hot spots. During
the monitoring period, PCB levels meas-
ured at a location upwind of Neal's Landfill
were <0.1 fjg/scm. The PCB levels found
at two locations downwind of Lemon
Lane Landfill ranged from 0.3 to 0.8
pg/scm. The downwind sampling  loca-
tions were  approximately 0.3 to 0.4 km
from the hot spots on the landfill. Back-
ground  PCB concentrations measured
upwind of Lemon Lane Landfill were <
0.1 fjg/scm. PCB levels determined at
locations designated  upwind and down-
wind of Neal's Dump did not show a
significant difference.  However,  the
samplers could  not  be placed at the
optimum upwind/downwind  locations
due to unavailability  of electrical power
and to  interference from the  heavily

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wooded area nominally downwind of the
landfill.
  At  Neal's Landfill and Lemon Lane
Landfill, measurements were performed
to determine the vertical distribution of
PCBs in the air above hot spots. PCB
concentrations measured at a  2  cm
elevation above hot spots at the two sites
ranged from 367 to 1108 //g/scm with a
median of 804 fjg/scm. The median con-
centration at  180 cm  elevation was 11
/jg/scm, seven times lower than at the 2
cm height. Variations in the vertical
concentration profiles at a given location
are probably due primarily to wind condi-
tions since the ambient  temperatures
were fairly uniform  throughout the var-
ious sampling days.
  In general, the procedures and equip-
ment used for the PCB monitoring per-
formed very satisfactorily and, based on
the QC/QA data, appear to have provided
high  quality results. Data recovery  for
measurements made with the low volume
sampling systems was 95 percent and for
the high volume sampler measurements
the data recovery was 76 percent. Data
loss  with, the high volume sampling
systems was due primarily to failure of
high  volume  sampler motors  and  the
motor generator units. Replacement of
the motor in  the  high volume sampler
with a by-pass type would significantly
increase the reliability of the high volume
sampling system.
  Weather during the entire period that
the PCB monitoring was performed was
unseasonably warm and dry. Daily high
temperatures  during  the  sampling at
Neal's Landfill and Neal's Dump on June
29 and 30 were about 32°C (90°F). During
the period July 12 through 21, high
temperatures on days that sampling was
performed were at or in excess of 38°C
(100°F). There  was no rainfall on  any
sampling day nor very little precipitation
during the interim periods. The results
obtained from this study probably repre-
sents "upper  limit" estimates of  the
airborne PCB levels.

Conclusions
(a) PCB levels measured at hot spots on
   the landfills exceeded upwind back-
   ground  levels, thus indicating that
   PCBs from the leaking capacitors are
   being emitted into the air.
(b) Based on measurements at hot spots,
   it appears that PCB emission levels
   are generally  correlated with  the
   number of exposed, leaking capaci-
   tors. In general, higher concentrations
   were  measured at locations where
   more capacitors were visible at  or
   above ground level.
(c) PCB concentrations which exceeded
   background (upwind) levels were ob-
   served at sampling locations down-
   wind of the landfills.
(d) Airborne PCB concentrations above
   hot spots vary with height; levels at 2
   cm above ground level are from 40 to
   100 times higher than the levels at an
   elevation of 180 cm.
(e) Unseasonably warm, dry weather that
   prevailed during the monitoring pro-
   gram probably maximized PCB emis-
   sions. Thus,  levels  observed during
   this study may represent "upper limit"
   values.

(f) The methodology employed to meas-
   ure PCB levels  in  the ambient  air
   performed  well. Quality  assurance
   data gathered during  the  study de-
   monstrates that both the low and high
   volume methods yielded reliable,  re-
   producible data and that comparable
   results are  obtained  by the two
   methods.
   D.  L. Sgontz and J. E. Howes, Jr. are with Battelle's Columbus Laboratories,
     Columbus, OH 43201.
   Barry E. Martin is the EPA Project Officer /see below).
   The complete report, entitled "A mbient Monitoring for PCB Near Three Landfills in
     the Bloomington, Indiana Area." (Order No. PB 85-233 492/AS; Cost: $14.50,
     subject to change) will be available only from:
          National Technical Information Service
          5285 Port Royal Road
          Springfield, VA 22161
          Telephone: 703-487-4650
   The EPA Project Officer can be contacted at:
          Environmental Monitoring Systems Laboratory
          U.S. Environmental Protection Agency
          Research Triangle Park, NC 27711

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