United States
Environmental Protection
Agency
Environmental Sciences Researc
Laboratory
Research Triangle Park NC 27711
Research and Development
EPA-600/S4-81-069  Oct. 1981
Project  Summary
Carbon  Monoxide  Commuter
Exposure  Data  Base:  A 5-Day
Study in  Los Angeles
William B. Petersen, Rodney H. Allen, Richard. A. Ziskind, and Michael B.
Rogozen
  Recent   concern  about  carbon
monoxide exposure to the commuter
population prompted the U.S. Envi-
ronmental  Protection  Agency  to
conduct a five-day field project  to
assess  the carbon monoxide  (CO)
exposure to Los Angeles commuters.
The purpose of this report is to docu-
ment the field project and to provide
the data collected during the project to
the public. The data collected include
measurements of interior CO, exterior
CO and  vehicle  speed  for  three
vehicles traveling  typical commuter
routes  during  the  morning  and
evening peak  traffic periods. In addi-
tion, hourly  average CO  measure-
ments were taken from eight  South
Coastal Air   Quality  Mangement
District fixed-site monitoring stations
and  six  California  Transportation
Agency vans  in the proximity  of the
commuter routes.
  This Project Summary was develop-
ed by EPA's Environmental Sciences
Research  Laboratory, Research Tri-
angle Park, NC, to announce key find-
ings of the research project that is fully
documented in a separate report of the
same title (see Project Report ordering
information at back).
Introduction
  During October 1  through 5, 1979,
Science  Applications  Incorporated,
under contract with  the U.S. Environ-
mental Protection Agency, conducted a
field study to monitor CO concentra-
tions both  inside and outside three
vehicles  traveling  typical commuter
routes in Los  Angeles County. The
vehicles traveled the typical commuter
routes during the morning  and  the
evening peak traffic periods. Two Inter-
scan continuous CO ajialyzers were
installed in each vehicle to monitor CO
levels simultaneously  inside  and
outside the vehicles. The outside samp-
ling probe was located near the fresh air
intake,  while the inside  probe  was
located near the driver's breathing zone.
The instrumentation, route selection,
monitoring  conditions, and observed
data are presented.
  The data collected  included recorder
time  traces  of  interior  CO  (COiNj),
exterior CO (COExr), and vehicle speed.
Accompanying  these   were  the
technician log sheets describing condi-
tions present as data were taken.
Conditions included  location, roadway
description, degree of traffic congestion,
and vehicle comfort  state.  In addition,
hourly average CO measurements were
taken from  eight South Coastal  Air
Quality Management District fixed-site
monitoring stations and six California
Transportation  Agency  vans  in  the
proximity of  the commuter routes
chosen.
  The full EPA  report describes  the
instrumentation used in the study, the.
route  selection  and experimental
design, and the development of the data

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     base. Appendices A and B in the report
     present the exposure and fixed site data.
     Appendix C describes the methodology
     used to estimate the one-minute aver-
     ages and Appendix D presents a graphi-
     cal display of the exposure data.


     Procedure
       The monitoring  periods and routes
     were chosen  to correspond to repre-
     sentative commuter trips throughout
     the  Los Angeles  area.  Although no
     specific  available "typical" commuter
     routes  have been published,  general
     knowledge of the traffic patterns, along
     with other factors such astraffic counts,
     was used to select vehicle routes. Each
     vehicle essentially simulated two com-
     muter  travel  patterns.  The  mileage
     driven was partitioned so that freeway
     and  arterial  driving  accounted  for
     roughly 80 to 20 percent, respectively.
     Furthermore,  the  routes all  traveled
     some portion of the "42-mile loop."This
     loop is instrumented by CALTRANS to
     provide  reaJ-time  traffic  volume and
     speed data. A final consideration was
     the  proximity of routes  to air quality
     monitoring stations. Since the latter are
     placed throughout the area, there was
     no problem in locating routes near fixed
     site stations.
       The three  Plymouth Valiants used
     traveled morning and afternoon com-
     muter  routes.  The  three   vehicles
     followed   the  prescribed   commuter
     routes as nearl.y as possible during the
     five-day study,  and  traveled over the
     routes as many times as possible during
     each three-hour period. Each half-hour
     during a commuter run, a new comfort
     state was established in the vehicle,
     according to a predetermined schedule.
     In order to provide an adequate descrip-
         tion of the measurement conditions a
         detailed recording of real time informa-
         tion  was  made.  An  unambiguous
         correspondence  among   CO  levels,
         vehicle  speed, and recorder observa-
         tions was made by assigning an alpha-
         betical  code to  each  notation  and
         simultaneously  marking  the  log  and
         chart papers by check  marks in the
         progressive code letter.
           Carbon  monoxide  was measured
         using  two  InterScan  1146  portable
         continuous analyzers in each vehicle.
         The InterScan device is a direct reading,
         battery   operated  unit  with integral
         sample pumps and battery charger. The
         detection element is an electrochemical
         voltametric sensor. The unit is designed
         for over eight hours of continuous field
         operation  between   recharges.   The
         detection ranges are 0 to 50 and 0 to
         100 ppm. The electrical output is con-
         nected  to  a  Soltec  VP-6723S 2-pen
         portable strip chart recorder. This device
         has a built-in battery charger and a
         glitch  marker  push  button  feature,
         which is useful for correlating recorder
trace location  with technicians'  log
comments.
  Instrumentation  for  vehicle  speed
measurements consisted of a magnetic
transducer pickup, pulse analyzer and
converter   circuitry,  and  a   Soltec
recorder. The pickup was  attached to
the front  right  disc brake' caliper. Its
output was a  pulse  train with  rate
proportional to the number of ventilator
rotor disc  slots  passing in a unit time.
This pulse output was converted to a
linear  analog   direct  current  voltage
which  provided the  Soltec  recorder
input.


Conclusions
  The full  EPA report does not provide
any data analysis or conclusions, but it
does provide a description of the experi-
ment and  a  hard  copy  of  the data
collected during the project. These data,
along with other data bases, will provide
researchers with the necessary tools to
characterize commuter  exposures to
automotive pollutants.
            The EPA authors William B. Peterson (also the EPA Project Officer, see below),
              Rodney H. Allen, Richard A. Ziskind, and Michael B. Rogozen are with the
              Environmental Sciences Research Laboratory, Research Triangle Park, NC
              27711.
            The complete report, entitled "Carbon Monoxide  Commuter Exposure Data
              Base: A 5-Day Study in Los Angeles," (Order No. PB 82-103 607; Cost: $9.50,
              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 Sciences Research Laboratory
                    U.S. Environmental Protection Agency
                    Research Triangle Park.  NC 27711
United States
Environmental Protection
Agency
Center for Environmental Research
Information
Cincinnati OH 45268
              Postage and
              Fees Paid
              Environmental
              Protection
              Agency
              EPA 335
Official Business
Penalty for Private Use $300

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