PB85-1U8682
EPA-600/4-84-088a
November 1984
INHALABLE PARTICTJLATE NETWORK REPORT:
OPERATION AND DATA SUMMARY (MASS CONCENTRATIONS ONLY)
Vol. I
APRIL 1979 - DECEMBER 1982
by
David 0. Binton, Jose M. Sune,
Jack C. Suggs and William F. Barnard
Environmental Monitoring Systems Laboratory
Research Triangle Park, North Carolina 27711
ENVIRONMENTAL MONITORING SYSTEMS LABORATORY
OFFICE OF RESEARCH AND DEVELOPMENT
U. S. ENVIRONMENTAL PROTECTION AGENCY
RESEARCH TRIANGLE PARK, NORTH CAROLINA 27711
NATIONAL TECHNICAL
INFORMATION SERVICE
n unanmni v COMMKI
SWWSflHI). ปป. 221M
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TECHNICAL REPORT DATA
(fltttf rttd Imarucnoiu on tkt revtrte btfart complerinfj
1. REPORT NO. 2.
EPA-600/4-84-088a
4. TITLE AND SUOTITLE
INHALABLE PARTICULATE NETWORK REPORT: Operation and
Data Sumnary (Mass Concentrations Only)--Volume I.
April 1979 - December 1982
7. AUTMORIS) '
David 0. Hinton, Jose M. Sune, Jack C. Suggs, William
F. Barnard
1. PERFORMING ORGANIZATION NAME AND ADDRESS
Environmental Monitoring Systems Laboratory
U.S. Environmental Protection Agency
Research Triangle Park, North Carolina 27711
12. SPONSORING AGENCY NAME AND ADDRESS
Environmental Monitoring Systems Laboratory
U. S. Environmental Protection Agency
Research Triangle Park, North Carolina 27711
3. RECIPIENT'S ACCESSIOWNO.
pr,- - ซ ;. o f. g 2 AftS
5. REPORT DATE
November 1984
6. PERFORMING ORGANIZATION CODE
:
10. PROGRAM ELEMENT NO.
i\. CONTRACT/GRANT NO.
13. TYPE OF REPORT AND PERIOD COVERED
Proiect Renort (1Q79-1QR?)
14. SPONSORING AGENCY CODE '
EPA/600/08
is. SUPPLEMENTARY NOTES publication as a two volume set is recommended. Volume II (Data
Listing) will not be required by all readers.
1ซ. ABSTRACT
This report is intended to serve as an ooerations overview and data summary
covering the operation of the 157 Inhalable Paniculate (IP) Network sites within the
United States. Volume I discusses the scope of the Network and instrumentation
utilized in the Network. Data (mass only) are traced from measurement through
processing and storage to routine reporting. Ouality assurance practices are also
given. Data summaries are provided. Volume II is a list of individual data upon
which Volume I is based.
Analyses, conclusions, and examples, either listed or indicated oy reference,
should orovide the reader with'both suggested uses and possible limitjtions of the
data. Chemical analysis of the collected particulate (sulfate, nitrate, and selected
metals) is part of IP Network objectives but those data will be the subiect of a
separate report.
17. KEY WOROS AND DOCUMENT ANALYSIS
a. DESCRIPTORS
Inhalable Particulate Network
Par^icula^e Data
Particulate Monitoring
Release Unlimited
b. IDENTIFIERS/OPEN ENDED TERMS
IB. SECURITY CLASS
c. COSATI Field/Group
21 NO. OF PAGES
210
22. PRICE
CPA Perm 2320.1 (ป-73)
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DISCLAIMER
The information in this document has been subject to the Agency's peer
and administrative review, and it has been approved for publication as an EPA
document. Mention of trade names or commercial products does not constitute
endorsement or recommendation for use.
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FOREWORD
Measurement and monitoring research efforts are designed to anticipate
potential environmental problems, to support regulatory actions by developing
an in-depth understanding of the processes that impact health and the ecology,
to provide innovative means of monitoring compliance with regulations, and to
evaluate the effectiveness of health and environmental protection efforts
through the monitoring of long-term trends. In support of these objectives,
the Environmental Monitoring Systems Laboratory (EMSL), Research Triangle
Park, North Carolina, has the responsibility for: assessment of environmental
monitoring technology and systems; implementation of agency-wide quality
assurance programs for air pollution measurement systems; and supplying
technical support to other groups in the Agency including the Office of Air,
Noise and Radiation, the Office of Toxic Substances and the Office of Enforcement.
ซ
In order to meet the 1977 Clean Air Act requirement for a reappraisal of
the National Ambient Air Quality Standard for particulate matter, EMSL, RTF
in conjunction with the U.S. Environmental Protection Agency's Office of Air
Quality -Planning and Standards, designed and implemented a nationwide monitoring
network to obtain the necessary data on which to base a proposed revision of
the particulate matter standard and to obtain data on inhalable particulates.
This document details network operations and summarizes data gathered during
routine operation of the 157 site Inhalable Particulate (IP) Network since
its beginning in April 1979 and continuing through December 1982.
Initially, the Network was designed to obtain data on particulates with
particle size less than or equal to 15 microns mean aerodynamic diameter. [n
1981, as a result of public comment, recommendations by the International
Standards Organization (ISO) Task Group and recommendations by the EPA Science
Advisory Board, emphasis was shifted from 0-15 (am to 0-10 \m aerodynamic
diameter size fraction. As of this publication 0-15 ym data collection has
been completed, 0-10 pro data collection is continuing. Upon receipt of one
year's data from each 0-10 pro site, the responsibility for [P data collection
will shift from EMSL, RTP to the respective Region. All EMSL [P sites are
scheduled for deactivation by the end of 1984.
Thomas R. Hauser, Ph.D.
Director
Environmental Monitoring Systems Laboratory
Research Triangle Park, North Carolina
111
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ABSTRACT
This report is intended to serve as an operations overview and data
summary covering the operation of the 157 Inhalable Particulate (IP) Network
sites within the United States. Volume I discusses the scope of the Network
and instrumentation utilized in the Network. Data (mass only) are traced
from measurement through processing and storage to routine reporting. Quality
assurance practices are also given. Data summaries are provided. Volume II
is a list of individual data upon which Volume I is based.
Analyses, conclusions, and examples, either listed or indicated by
reference, should provide the reader with both suggested uses and possible
limitations of the data. Chemical analysis of the collected particulate
(sulfate, nitrate, and selected metals) is a part of IP Network objectives
but those data will be the subject of a separate report.
IV
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CONTENTS
Disclaimer ii
Foreword iii
Abstract iv
Figures vii
Tables viii
1. Introduction 1
1.1 Background 1
1.2 Purpose of Report 4
2. Summary and Conclusions 8
3. Network Design 10
3.1 Rationale 10
3.2 Network Operations 11
3.2.1 Site Selection 11
3.2.2 Instrument Selection 12
3.2.3 Sampling Operations 17
3.3 Sample Collection and Validation 17
3.4 Data Validation 18
4. Quality Assurance 22
4.1 Introduction 22
4.2 Internal Quality Control and its Relationship to
Quality Assurance 22
4.3 Internal Quality Assurance 24
4.4 External Quality Assurance 24
4.4.1 Overview 24
4.4.2 Flow Rate Performance Audits of IP Samplers. . . 28
4.4.3 Audit Results 28
5. Data Summary and Assessment 36
5.1 Data Accuracy 36
5.2 Data Precision 36
5.2.1 Presentation of Precision Data 37
5.2.2 Inference 38
5.2.3 Data Presentation 43
5.2.4 Data Processing 44
5.3 Results 44
References 45
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Appendices
A. Inhalable Particulate IPN Data, Percentile Rank Frequency
Distribution (Entire Network)
B. Inhalable Particulate Network Percentile Rank Frequency
Distribution (Individual Sites)
C. Inhalable Particulate Network Data Suomary by Site
D. Inhalable Particulate Site Listing with Pollutants
Sampled and Site Description
E. Inhalable Particulate Network Sampler Calibration Data
F. Inhalable Particulate Network Quality Assurance Flow
Audits (% Difference)
VI
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FIGURES
Number Page
1 Thoracic/Extrathoracic Particle Size Distribution 1
2 Typical Ambient Aerosol Size Distribution (Typical
Atmospheric Particle Distribution; Particle Respiratory
System Deposition) 3
3 IP Sites (PM1Q and PM15) Operated during 1979-1982 6
4 TSP Hi-Vol Used in IP Network 14
5 SSS Hi-Vol Used in IP Network 14
6 Manual Dichotomous Sampler Used in IP Network 16
7 Example IP Calibration Curve 27
8 Example IP Calibration Interpolation Chart 27
9 Example High Volume Sampler Audit Data Sheet 29
10 Example Dichotomous Sampler Audit Data Sheet 30
11 High Volume Sampler Flow Audit Accuracy 1979-1982 Jl
12 Size Selective Inlet Flow Audit Accuracy 1979-1982 32
13 Dichotomous Sample Total Flow Audit Accuracy 1979-1982 ... 33
14 Dichotomous Sampler Coarse Flow Audit Accuracy 1979-1982 . . 34
VII
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TABLES
Number Page
1 Example of OA Listing 19
2 Concentration Ranges Used to Screen Particulate Data
for Further Examination 20
3 Typical S.A.S. Analysis 21
4 Operator Training Check Sheet 25
5 Operator Training Check Sheet Instructions 26
6 Hi-Vol and SSS Collocated Data Coefficients of Variation . 40
7 Manual Dichot Collocated Data Coefficients of Variation. . 41
8 15 Micron and 10 Micron Dichot Collocated Data Coefficients
of Variation 42
Vlll
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SECTION 1
INTRODUCTION
1.1 Background
The 1977 Clean Air Act Amendment requires a reappraisal of the National
ambient air quality standard for particulate matter. In order to meet this
requirement, information regarding both Total Suspended Particulate (TSP) and
smaller particles was required. Research into the health effects of particles
suspended in ambient air increasingly focused on the smaller particles.
Smaller particles not only penetrate deeper into the human lung, but they are
also more difficult for the body to remove, thus body retention time and
clearance routes are sufficiently long to increase the probability of damage.
These smaller particles are generally referred to as inhalable. Figure 1
illustrates that although particles up to 200 M are inhaled, those particles
above 20-25 M"i are retained in the extrathoracic region (mouth, nose, etc.)
and do not reach the deep lung.
A further reason to examine the smaller particles is indicated from the
bimodal distribution of the large and small particles as found in ambient air
(Figure 2). Naturally occurring dust particles of greater than 10-15 Mm
diameter are collected by the standard High Volume Sampler .(Hi-Vol). These
particles, therefore, add to the mass collected and together with man-made
particles may create TSP concentrations which exceed the current TSP standard
of 75 Mg/1"3 annual geometric mean. In 1978 over 400 areas in the United
States did not meet the TSP standard possibly because of mass contributed
by naturally occurring particles.
Thus, for two reasons, EPA perceived a need to obtain data on smaller
particles. They are: (1) physiological studies have shown that the human
lung collects an appreciable percentage of particles at and below 15 pro mean
aerodynamic diameter with extremely small particles (2 to 3 pm) reaching the
gas exchange area of the Lung1. The deposition efficiency versus particle
size is given in Figure 2 for the alveolar region of the human Lung. (2) the
Hi-Vol collects particles above 15 |jm such as naturally occurring dust2.
EPA's Environmental Monitoring Systems Laboratory (EMSL), Research
Triangle Park, N.C. in conjunction with EPA's Office of Air Quality Planning
and Standards was given the responsibility of providing ambient air data for
the small particle size range. The exact value for the upper limit, however,
was and still remains, controversial. Therefore, data from both the original
0-15 Mm samplers and the subsequent 0-10 \im samplers are included. In 1977-78
when the Inhalable Particulate (IP) Network was being planned, the major
monitoring emphasis was on collection devices which could provide measurements
1
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Ill II III
BOUNDARY OF INSFIRAILE FRACTION
EXTRA THORACIC
CONVENTION
0.7 1.0 23 S 7 10 20 30
PARTICLE AERODYNAMIC DIAMETER (i.itm
Figure 1 . Thoracic/extrathoracic retention vs. particle size distribution. (From Lippman,
Morton: Size Selective Health Hazard Sampling, Chapter H; Air Sampling Instruments
for Evaluation of Atmospheric Contaminants, 6th Ed., ACGIH. pg. H-13. 1983).
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u
HI
I I I
PARTICLE DISTRIBUTION
-PARTICLE DEPOSITION
I I I _
*l>x
u-
0.1
15
1.0
FINE FRACTION
5 7 10
COARSE FRACTION*!
-INHALED PARTICIPATE
PARTICLE DIAMETER, urn
20
IS
Figure 2. Typical ambient aerosol size distribution and particle respiratory
system deposition. (Rodes, C.E., Inhalable Paniculate Network, Overview
of Network Operations, Environmental Monitoring Systems Laboratory,
Research Triangle Park, NC, unpublished, June 10, 1979).
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of ambient air concentrations attributed to 15 pm (and smaller) particles and
2.5 Mm (and smaller) particles. For these reasons instruments using inlets
designed by McFarland3 (single cut) and Wedding4 (dual-cut) were evaluated
and utilized.
In 1981, after reviewing EPA's Clean Air Science Advisory Committee's
recommendations1 and the concurrent International Standards Organization
(ISO) Task Group recommendations (specifically, Technical Committee 146-Air
Quality5), EPA's Office of Air Quality Planning and Standards recommended
that the revised particulate matter primary standard for ambient air should
be based on a 10 urn size criteria. The fraction below the 10 (jm cut, desig-
nated by EPA as PM.,Q was anticipated to replace the existing TSP standard.
EMSL, RTF, responded to the 10 urn recommendation by adding to or replacing
existing 15 Mm equipment with instruments modified to sample 10 \m and smaller
particles. Early published reports referred to the Inhalable Particulate
Network as IPN. This and subsequent reports use PM]C. and PM,Q to distinguish
between 15 pm and 10 |jm samplers or data respectively.
It is important for the reader to understand that PM,,- or PM,Q data are
data collected by a sampler designed to have a cutpoint (D
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Data collection began in April 1979 and continues as of this writing,
although the latest data provided in this report is December, 1982. By
providing sampling procedures, quality assurance flow check audit procedures,
data handling procedures, data acceptance/validation procedures, sampler
precision estimates, etc. the reader should better understand how to utilize
these data in his own specific analyses. A conscious effort was made to
limit data analyses to only those areas were data summary would aid in data
explanation. Represented in this report are 525 equivalent sampler-years of
data (i.e., one sampler operated one year). Beginning in 1979, 57 PM.., sites
were started and some are still in operation today. Others were started and
quickly stopped due to loss of the site (re-roofing the building, sale of
property, loss of operator, etc.). Equipment problems caused the invalidation
of a substantial amount of data, especially those problems associated with
instrument malfunction and with improper assembly by the manufacturer of the
dichotomous sampler impactor assembly (A.E. Bond, EMSL/EPA, personal communi-
cation, May, 1982).
In reviewing the data, one can follow the evolution of the PM-ic Network
starting in 1979 with 57 sites; growing eventually to 157 sites; converting
to PM1Q in 1982; and shrinking to 63 sites in 1983; further decreasing to 20
sites in 1984 with termination scheduled in 1985. Figure 3 gives the geo-
graphical location of all 157 sites. A list of sites is provided in Appendix
D. *
Although the network was developed and managed by EMSL/RTP, actual
sampling was conducted by approximately 1,000 State, county, or local agency
on-site personnel. For the most part this sampling effort was undertaken in
addition to local agency responsibility, thus local personnel and budget cuts
had a direct impact on data collection. The reader, therefore, will notice
that data are missing in some areas. Where appropriate we have given reasons.
These "reasons" are not intended to be either excuses or apologies, but
rather to document that missing data were a consequence of operational con-
straints rather than deletion on the basis of subjective or judgemental
interpretation of the data. Furthermore, if a datum value passed all
validation procedures but the value was unusually high or low, the value was
still retained even though it would become an outlier under almost any
statistical analysis.
A secondary purpose of this report is to provide all individual validated
PM^, and PM,Q mass concentration data through December 1982. These data are
listed in Innalable Particulate Network Report: Data Listing (Mass Concentra-
tions Only) Vol. II April 1979-December 'ฐft? (Hi rf*rf mp')f"- n^-ซ"ซ; of
these data are available via public file
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Instruments for Evaluation of Atmospheric Contaminants, 6th Edition, Chapter
L, American Conference of Govemental Industrial Hygienists, Cincinnati,
Ohio, 1983. (4) "Estimating PM-Q Concentrations from IP and TSP data", by
T.G. Pace, APCA 82-45.2 proceedings of 75th Annual APCA Meeting, Philadelphia,
PA, June, 1982. (5) "Characterizing Ratios of Participate Concentrations:
A Preliminary Step in Assessing Likely Attainment Status under a PM.. NAAQS",
by Anthony D. Thrall, SAI, April, 1983. (6) "Potential Causes of Elevated
PM1 and PM15 Concentrations in the IP Network", J.C. Watson, Draft Report*,
Desert Research Institute, 1983. (7) "Analysis of Particulate Matter Concen-
trations and Visibility in the Eastern U.S.", by John Trijoinis, Sauta Fe
Research Corp., EPA-450/4-84-008, August, 1983. (8) "Spatial Characteristics
of Inhalable Particles in the Philadelphia Metropolitan Area", by Jack C.
Suggs and R.M. Burton, JPCAAC 33(7)637-726 (1983), July, 1983. (9) "Prelim-
inary Assessment of the PM-i. Data from Eight Locations in the United States",
by C.E. Rodes, and E.G. Evans, Draft Report*, EPA, 1984). The above documents
deal with various subsets of the data presented herein, therefore, conclusions
based on the data subset may be either strengthened or weakened when one
includes the complete data set.
*Reports in draft stage are generally not available until finalized.
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SECTION 2
SUMMARY AND CONCLUSIONS
Data from the EMSL, RTF Inhalable Particulate Network is presented
herein. Individual values for TSP Hi-Vol; PH., Dichotomous Coarse, Fine, and
Total; and PH.. SSS mass are presented. Ratios of Dichotomous Total-to-TSP
.. .
Hi-Vol, and SSS-to-TSP Hi-Vol are summarized for PM..- mass. Similar data are
presented for PM... sampling but on a smaller number 5f samples. (More PM.
samples will become available as PM. Q sampling continues throughout 1984) .
Quality Control and Quality Assurance procedures and results are presented
and used to estimate sampling accuracy by examining sample flow rate, weighing
accuracy, etc. Overall sampling accuracy is difficult to determine directly
because the measurement requires the production of accurately known concentra-
tions of particulate matter of a wide variety of sizes. For a more detailed
explanation of sampling accuracy and potential error sources the reader is
referred to Air Quality Criteria for Particulate Matter and Sulfur Oxides ,
Volume II, U.S. EPA, ORD, Environmental Criteria and Assessment Office,
Research Triangle Park, N.C. , EPA-600/8-82-0296, December, 1982. Particulate
matter is discussed in referenced Chapters 2 and 3. A summary is given in
referenced Section 3.3.7.
Data precision is discussed using paired data obtained from collocated
instrument sampling. The signed percent difference of the two measurements
(expressed as R) was obtained by dividing the difference between the data
pair by the average of the two measurements and multiplying by 100.
Student's t statistic was used to test the Null Hypothesis that R = 0 (i.e.,
that the relative bias is zero over each data set).
The value of t was statistically significant at the 5% level for one or
more sites within each sampling class (Hi-Vol, SSS, Dichot-,.) meaning that
the differences between paired instruments is probably real. Converse Ly at
least one site within each class was aot significant at the 5% level. Overall
there is substantial variability but little bias across the entire collocated
data set.
The general contention that suspended particulates are a complex mixture
of large and small particles, both naturally occuring and man made, is supported
by the absence of a simple, consistent ratio of IP to TSP. If the IP were a
simple fraction of TSP, a consistent ratio would be expected and estimates of
IP from past TSP would have been possible. That this is not the case and
that IP is a complex fraction of TSP is supported both by the referenced
publications in Section 1.2 and by the data presented herein.
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The authors do not infer that for a specific site, a consistent ratio of
IP-to-TSP is impossible. If a given site is influenced by particulates
originating from a specific source, then the inhalable fraction may possibly
be a consistent sub-set of TSP. For instance, if Dichot Total and TSP
concentrations are paired, one can investigate the ratio of PM...-to-TSP. An
example when IP is a consistent subset of TSP is Lompoc, CA (054080002) where
77 samples were compared (Appendix C, page 8). The minimum ratio was 40%
(.4) with a maximum at 93%. The mean was 56% with a standard deviation of
the ratios of 9%. For a different site, the ratio-of-means would be different.
The ratio-of-means for PM -to-TSP varies from 32% in St. Paul, MN
(243300003) (Appendix C, page 27) to 127% in Philadelphia, PA (397140032)
(Appendix C, page 46). The ratio-of-means for PM]0-to-TSP varies from 30% in
Steubenville, OH (366420012) (Appendix C, page 40}to 191% in Boise, ID
(130220003) (Appendix C, page 16).
There are examples where the individual sample-pairs (and multiple
sample means) are extreme e.g. Dichot - Total-to.-TSP =2.93 (293%) in Eugene,
OR (380560013) (Appendix C, page 42) and Dichot -Total-to-TSP = 6.35 (6351)
in Boise, ID (130220003) (Appendix C, page 16). These extremes are based on
real validated measurements, yet they violate the basic principle that Inhalable
Particulates are, in fact, a subset of Total Suspended Particulates.
There are several potential explanations for these extremes:
(1) ONE OR BOTH DATA VALUES ARE IN ERROR. This is a possible explanation.
The data were not removed, however, because they passed the validation
criteria. Further, a determination of which value to remove was
not possible. To have removed both would nave been a subjective
decision applied only to the extreme values.
(2) THE ACTUAL PARTICULATE CONCENTRATION PRESENTED TO EACH INSTRUMENT
VARIED SUBSTANTIALLY. This violates the presumption that the
particulate is well mixed and homogenious in the microenvironment.
(3) THE INSTRUMENTS DO NOT MEASURE THE EXPECTED SIZE RANGE OF PARTICULATES.
To some degree this is supported due to the orientation and wind
speed dependence of the TSP Hi-Vol as reported by McFariand and
Rodes9.
Perhaps these extreme ratios emphasize the requirement for careful,
statistical analysis of IP data prior to using the data for decision making
purposes. Certainly, at any given site, a ratio of IP-to-TSP is mathematically
possible but the actual value is dependent upon which (if any) outliers are
identified as flawed and not used in the computations. Further experience
with the operation of these samplers and with the interpretation of the
resulting data will be needed to resolve the questions raised and to expand
upon the conclusions that can be drawn.
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SECTION 3
NETWORK DESIGN
3.1 Rationale
In 1978, the data from the Inhalable Particulate Network were anticipated
to be used primarily to assist in a revision of the existing Total Suspended
Particulate Standard to a standard based on the specific particle size range
of 15 jjrn mean aerodynamic diameter and below, and to a lesser degree to
provide information on the possible sources of the particles for subsequent
control strategy implementation. To accomplish this, establishment of a
nationwide network of 200 air monitoring sites over a three-year period was
planned. However, due to resource constraints, only 157 sites were placed on
line.
The following specific Network objectives and design criteria were
provided by the Office of Air Quality Planning and Standards (OAQPS): (a)
conduct a pilot program to demonstrate that the monitoring technology was
adequate to proceed (technology to make routine size-specific aerosol measure-
ments had only recently become commercially available), (b) provide monitoring
support to on-going epidemiology studies wherever possible, (c) provide
background data for non-urban and rural sites, (d) monitor fugitive dust
locations, (e) select urban sites with priorities primarily for population
density and non-attainment of the current TSP standard, (f) at all sites,
measure the mass concentration of TSP and IP, (g) at selected sites, measure
the fine and coarse components of IP (i.e., PM._), and (h) provide for a
Limited component analysis scheme beyond mass concentration to further
characterize the data base. Later a final objective was added: (i) incor-
porate PM,n technology into the network for data collection in the 0-10 \Jtrn
size range.
OAQPS specified the candidate cities. With OAQPS .ipprovai, EMSL and/or
an EMSL contractor made the specific site selection within the city, based on
desired site classification (Commercial, Residential, Industrial, Rural,
etc.) and specific site availability.
All of the objectives and constraints were combined into a protocol of
network operations, which was prepared prior to network implementation. This
protocol10 included the various aspects of network design and setup, sample
collection, analyses, quality assurance, maintenance, and data processing and
analyses. All operations except the actual collection of samples would be
provided by EPA. Manpower was to be provided by State and local agency
personnel to implement the operation of the sampling equipment. Because of
the limited manpower available within EPA, contractor support was also planned.
A Quality Assurance program was planned and budgeted at 5-10% of resources.
10
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3.2 Network Operations
3.2.2 Site Selection
Although each sampling site location was physically evaluated
against the siting criteria given in the Infaalable Particulate Network
Operations and Quality Assurance Manual11, March, 1983, administratively the
selection process was quite variable. Land owner permission, local agency
approval, Regional Office concurrence, OAQPS recommendations/concurrence all
had to occur in order for a specific site Co begin and continue sample/data
collection. Further, since more than 1000 people were eventually involved
directly in the data gathering activities, their performance, interest, and
assistance directly affected the amount and quality of data collected.
Equally important was the staffing level at EMSL. As the program grew, PM -
Size Selective Samplers (SSS)* and PM..- Dichotomous Samplers were added.
Because any large network has delays and false starts, one can find specific
instances where EMSL did not provide prompt response to a field problem.
Similarly, one finds examples where field problems were not communicated to
EMSL for corrective action. The point to be made is not that problems occurred,
but that overall, in spite of the diverse demands on time, personnel, and
resources, EMSL received excellent cooperation from Local, State, and Regional
personnel. This cooperation resulted in data collection from 525 sampler-years
from 157 sites in the geographical locations as shown in Figure 3. Appendix
0 gives the SAROAO number, Region, State, Site Name, Instrument Complement,
Type, Location, Land use, and Elevation for each site.
All sites provide routine TSP data from a Hi-Volume sampler and PM15
data from either an SSS or Oichotomous Sampler. In addition to routine PM..,.
and PM.,. sampling requirements, EMSL utilized selected sites for intercompar-
ison of instruments. At various times a given site became one or more of the
following:
1. Comparison Site: In addition to the instrument complement of a PM..,. and
a TSP HiVol for routine sampling, some of the initial sites were provided
with additional PM.,. instruments. These special sites provided data for
comparison of SSS-to-Qichotomous, etc. Eventually L28 sites had boch SSS and
Oichotomous 15 instruments. These are identified in Appendix D.
2. Collocated Site: A site containing duplicate instruments of the same
type and usually by the same manufacturer. Duplicates include Dichotoraous
PM 5 to Dichotomous PM,,-, TSP-to-TSP, SSS ,,-to-SSS ,., Dichotomous PM to
Dicnotomous PM.... The following sites were utilizes for collocated
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SAROAD #
010380023
030600002
061260001
222160011
222640016
330660010
333520001
341160006
366420012
397140003
397140037
491840057
3.
STATE SITE
AL N.Birmingham
AZ N. Phoenix
CO Lakewood
MA Springfield
MA Worcester
NY Buffalo (PS 28)
NY Buffalo (Wilmuth Pump)
NC Durham
OH Steubenville
PA Phila. (Broad)
PA Phila. (U. Temple)
WA Seattle (Duwamish)
TSP-to-TSP SSS-to-SSS DICHOT-to-DICHOT
.X
X
X
X
X
X
X
X
X
X
X
X
X
X
Key Site: An existing PH.. site which was augmented with a PM,Q
The objective for a key site is to provide data for both PM15 and PH,
nine sites designated as key sites are listed below:
10'
monitor.
The
SAROAD # STATE SITE
Q10380023
030600002
056535001
330660010
341160006
366420012
396620001
397140003
452560034
AL
AZ
CA
NY
NC
OH
PA
PA
TX
N. Birmingham (S.20th)
Phoenix (Roosevelt St.)
Rubidoux (Mission Blvd)
Buffalo (PS 28)
Durham (Cameo)
Steubenville (Wash1ton)
TYPE
Center City, Industrial
Center City, Commercial
Rural, Commercial
Center City,' Industiral
Center City, Industrial-
Center City, Residential
Suburban, Industrial
Pittsburgh (N.Braddock)
Philadelphia(500 S.Broad)Center City, Commercial
Houston (CAMS-1) Suburban, Industrial
Site considerations based on type (as shown above) range from expected low
particulate levels in "Rural" land usage to expected high levels in "Center
City". Appendix D gives land usage by Type for all 157 sites.
3.2.2
Instrument Selection
3.2.2.1 Introduction
There were two original requirements for the IP Network. The
first requirement was to collect PM., data at all sites. The second was to
collect a sample year of comparison lata for both TSP and PM,, to establish
an IP/TSP relationship. Later the PM., requirement was extended to include
PM.., therefore, equipment modifications were made and sampling dates were
extended.
In early 1978, when the IP Network was being planned, a
recently developed dichotomous sampler was available and was incorporated
into the network. This sampler (described in more detail in Section 3.2.2.4)
provided two particle size fractions. The larger size fraction (Coarse)
included particles from 2.5 to 15 pm mean aerodynamic diameter. The smaller
12
-------
size fraction (Fine) included particles below 2.5 |Jm. When added together,
the Fine and Coarse fractions give a "Total" inhalable concentration in the
0-15 pa range (PM..,). Typical size distributions of the Fine and Coarse
fractions are given in Figure 2. While the small fraction, "Fine", is not a
requirement for defining an Inhalable Particulate Standard per se, it is
useful in determining the origin of particulates.
The dichotomous sampler was therefore selected as the initial
PM,, sampler because of availability and dual size range fractions. It was
(ana is) suitable for providing IP concentrations and, when paired with the
standard Hi-Vol, IP/TSP relationships can be developed. The dichotomous
sampler is more complex than the Hi-Vol and the two sample fractions (Coarse
and Fine) require twice the sample handling, weighing, calculation, etc. as
the Hi-Vol. Alternate samplers were therefore investigated. One PM , sampler,
the Size-Selective Sampler (SSS), was developed as a modification to a standard
Hi-Vol and tested at 50 of the first field sites. This modified Hi-Vol
sampler is identical to the TSP hi-vol except that the gable roof is replaced
with a special inlet and the filter faceplate is removed. The SSS was developed
as a mono-cut sampler offering ease of operation, single sample, large sample
size, and associated cost savings.
3.2.2.2 TSP Hi-Vol Sampler
The TSP high-volume (Hi-Vol) sampler (General Metals Model
2310-105 o'r equivalent12) used in the IP Network was equipped with a mass
flow controller, electromechanical elapsed time meter and flow recording
device. (See Figure 4.) The nominal operating flowrate is I.42 m /
min (50 cfm). The filter medium was micro-quartz in 1979 and glass fiber
from 1980 through 1982.
3.2.2.3 SSS Hi-Vol Sampler
The 15 micron Size-Selective Sampler is a TSP Hi-Vol as described
previously, equipped with a special inlet instead of the standard gable root
to collect 0-15 micron (aerodynamic diameter) particulate. (See Figure 5.)
This inlet was designed by Dr. A. E. McFarland of Texas A&M University and LS
currentjly available commercially. The nominal operating flowrate LS
1.13 m /min (40 cfm). The only significant changes from the TSP Hi-Vol
(other than the inlet) are the elimination of the faceplate and hold-down
screws, which are replaced by a spring clamp mechanism. Filter media were
the same as used on TSP Hi-Vol above.
3.2.2.4 Manual Dichotomous Sampler (PM g)
The dichotomous sampler LS a Low flowrate 16.7 L/min (.59 CFM)
sampler which splits the air stream passing through the 15 micron inlet Lnto
two separately filtered portions. It is often referred to as a "virtual"
impactor since the particle size separation is accomplished by pseudo-
impaction into an air stream of differing velocity, rather than onto an
impaction surface. The PM.., dichotomous samplers cut the 0 to 15 micron
total sample into 0 to 2.5 micron FINE and 2.5 to 15 micron COARSE fractions
which are collected on separate 37 mm (diameter) Teflon filters. The FINE
and COARSE concentrations are determined gravimetrically and are combined.
13
-------
FLOW
FILTER
FLOW
CONTROLLER
FLOW RECORDER
(OICKSON CHART)
WEIGHT:-65 Ib DIMENSIONS: ~iadw
INLET COVER
Figure 4. TSP high volume sampler used in IP network.
INLET
FILTER
FLOW
CONTROLLER
.FLOW
'RECORDER
*> STD. HI-VOL
SAMPLER
14 WEIGHT:~95lh
DIMENSIONS: ~
Figure 5. SSS high volume sampler used in IP network (0 - 15 \an cut).
14
-------
mathematically to give the TOTAL IP fraction. The Sierra Model 244 and
Sierra Model 244E were the two models of manual dichotomous samplers used in
the IP network in 1979.
Both Sierra Model 244 and 244E Manual Dichotonous Sampler
consist of two modules, the sampling module and the flow control module. In
the Model 244, the flow module is equipped with a flow controller, digital
timer/programmer and elapsed time indicator. The sampler module consists of
the sample inlet, "virtual impaction" chamber, two 37 mm filter holders,
vacuum lines, and tripod support. The 37 mm diameter Teflon filters are
shipped from the lab in nylon cassettes for ease of loading and removal by
the operator from the sampler module. The filters remain in these cassettes
during sampling and shipment.
The Sierra Model 244E sampler became the predominant Dichotomous
Sampler used in later years. The Model'244E is the same basic sampler as the
Model 244 with the exceptions that the flow module has a mechanical 7-day
timer, and modifications have been made to the flow system to aid in rotameter
flow calibration. A diagram of the Sierra Model 244E dichotomous sampler is
shown in Figure 6.
3.2.2.5 Automated Dichotomous Sampler (PM..,)
An automated version of a PM,,. dichotomous sampler (manufactured
by Beckman Instruments) was used initially in the IP Network, but was Later
replaced with manual samplers because of ease of operation and reliability.
This sampler utilizes the same basic virtual impaction system found in the
manual dichotomous samplers. The major differences between it and the manual
model are multiple samples for a given time period and a built in flow sensor
to detect filter overloading.
3.2.2.6 Manual Dicnotomous Sampler (PM,^)
~~~ " -- - 1U
The information given in Section 2.2.2.4 refers equally to
PM _ dichotomous samplers except that the inlet is designed to reject particles
above 10 microns. The fractions therefore become 0-2.5 pm and >2.5-10 pro.
3.2.2.7 Site Operation
Each site was equipped with an electro-mechanical timer to
turn all samplers, except the automated dichotomous sampler, ON and OFF at
the same time. All instruments were set initially to the proper flowrates
using their respective flow calibration tables. Except in special cases all
samplers were operated every sixth day for 24 hours from midnight to midnight
on the same schedule as the National Air Monitoring Stations (NAMS) or State
and Local Air Monitoring Stations (SLAMS) samplers. Except tor special
studies (e.g., Philadelphia), operation was allowed only on the day scheduled.
Alternative (make-up) days were not used.
15
-------
40"
CONTROL MODULE
50 IBS.
MODEL 244
MODEL 244E
AIRFLOW
10 Jim
FRACTIONATING
INLET
FINE Id ACCELERATION
PARTICLE flL^^-" NOZZLE
TRAJECTORY -
COARSE
PARTICLE
TRAJECTORY CjlJvsj \COLLECTION
NOZZLE
PARTICLE 8 FIN6 PARTICLE
FILTER
(ARTICULATES <2JS Mm
a ^ARTICULATES 2^-10.0 Aim
Figure 6. Manual dichotomous sampler used in IP network - Sierra Model 244 and 244E.
16
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3.2.3. Sampling Operations
The mass concentrations provided in this report came from the 157
PM1- and PM.Q sites shown on the map in Figure 3. This network includes a
variety of sites such as commercial, industrial, and rural sites as indicated
in Appendix D.
Data obtained from April 1979 through December 1982 are shown in
summary form in Appendix C. Daily values are given in "Vol. II, Inhalable
Particulate Network Report: Data Listing (Mass Concentrations Only) April
1979 December 1982". Samples were collected at each site on an every 6th
day schedule and mailed to a central EPA laboratory in the Research Triangle
Park for analyses. All samples were analyzed for mass, while every fourth
sample was selected for subsequent component analysis (e.g., sulfate, nitrate,
selected metals). This report does not include any results except mass
concentration. Analytical results will be the subject of a separate report.
Approximately 80 to 85% of the 1500 samples/month were considered
valid for mass determination and subsequent component analysis. Of the 15 to
20% invalid samples, about half were caused by reasons such as sampler or
power failure. The balance of the invalid samples were voided because of
calculational errors, incomplete data, and excessive variability in sampling
parameters, or other instrument problems. One major instrument problem was
the omission of an internal o-ring by the dichotomous sampler manufacturer.
This o-ring is used to provide an airtight seal between the two dichotomous
air chambers. This presented an error not detectable by normal calibration
or QA procedures and could be discovered only by disassembly of the impactor
section. This problem alone accounted for 880 data values being declared
void. v
3.3 Sample Collection and Validation
Routine network operations began with the RTP contractor laboratory
pre-weighing all filters in a controlled environment. The filters were Chen
distributed to network monitoring stations. These filters were used to
collect ambient samples from TSP high volume, size selective high volume, and
dichotomous samplers every six days according to the NAMS/SLAMS schedule.
After collection, the filters were packaged and returned to EMSL's RTP contractor
for analyses. The filters and accompanying data cards were checked against
criteria11 which help detect sample, sampling, and/or equipment problems.
These criteria cover torn filters, gasket Leaks, flow leaks, incorrect sampling
time, incorrect date sampled, and receipt of sample within six months atter
sampling. The six months time limit was required and imposed in order to
meet validation criteria to complete the data base within one year after
sampling.
The filters were then forwarded to the laboratory for final (post-)
weighing. After weighing, the filters were either archived or marked tor
component analyses. The post-weights were recorded, paired with the pre-
weights and flow volumes, and appropriate microgram per cubic meter values
were calculated. These values were converted to SAROAD13 format, and stored
in the computer system.
17
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3.4 Data Validation
Preliminary validation listings were produced froa the raw data and
called OA listings (Operating Agency listings, see Table 1). These preliminary
listings were produced for screening of suspect values and distributed to the
participating Operating Agencies. The corrected OA listings were used to
produce the final validation listings.
Two tests were used to identify unusually high values, low values, and
values inconsistent with concurrent pollutant levels for the same site and
day. These were the Grubbs14 test and SAS15. The statistical outlier test
used initially was the Grubbs test. The Grubbs test is based on one or more
values being too large or too small when compared to the average and assumes
a normal distribution. Using the Grubbs test for sites with less than 10
days of samples, only maximum and minimum values were examined. For sites
with 10 to 18 days of samples, the upper two and lower two values were examined.
For sites with more than 18 days of samples, the highest 3 and lowest 3 days
were examined as possible outliers. Any value determined to be any outlier
by the Grubbs test was flagged and included in the printout of the individual
results (OA listing). Potential outliers are not necessarily incorrect
values, but values which require closer scrutiny before being included in the
valid data set. These "flagged" values or outliers, therefore, were not
removed from the data set unless a specific reason was identified which would
cause invalidation of the data value.
Because IP is a fraction of TSP, the ratios of IP to TSP were thought
useful for validation purposes. The ratios SSS-to-TSP (SSS/TSP), Oichotomous
Sampler Total-to-TSP (Total/TSP), Dichotomous Sampler Total-to-SSS (Total/SSS),
and Dichotomous Coarse-to-Dichotoraous Fine (Coarse/Fine) ratios were used.
The acceptance ranges used to screen sampling data are shown in Table 2 and
were based on previous sampling experience prior-to implementation of the
Network. Reliance on strictly statistical tests such as the Grubbs test
along with predetermined acceptance ranges was abandoned in favor of.flagging
and investigating extreme values for each data set. This was accomplished
with the aid of SAS15 software. Table 3 is an example of a univariate statistical
summary provided by SAS and used for flagging potentially invalid data. If
the flagged data were not invalidated because of documented instrument malfunction,
calculation error, operator error, flow rate out of tolerance, improper
sample date or time, torn or damaged filter, weighing error, and/or improper
sample identification, they were accepted as valid. Further, mass concentrations
are reported as calculated with no adjustment for the small and variable
errors associated with sulfate and nitrate artifact formation on glass fiber,
quartz, and teflon filters.6
18
-------
TABLE 1. EXAMPLE OA LISTING
Inhalable Particulate Network
Environmental Protection Agency
*** Not Validated ***
Virginia
APC Division of Health Department
LOCATION/SITE
SITE & TIME START
ADDRESS CODE HOUR DATE TOTAL
FINE
COARSE
Fairfax/482630001 A07
Great Falls, 925 Springvale Rd. * ป
MASS
MASS
MASS
MASS
MASS
MASS
7
7
7
. 7
7
7
00
00
00
00
00
00
80/09/06
80/10/12
80/10/24
80/11/05
80/11/17
80/11/29
49.9
14.9*
22.3
17.4
19.8
10. 6*
37.7
6.8*
9.8*
9.9*
16.5
8 . 2*
12.2
8.1
12.5
7.5
3 . 3*R
2 . 4----R
* = Value out of Limits
R = Ratio out of Limits
19
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TABLE 2. SAMPLING PARAMETERS AND CONCENTRATION RANGES USED TO
SCREEN PARTICULATE DATA FOR FURTHER EXAMINATION
Sampling Rate
Sample Type
Hi-Vol
SSI
Dichot-Coarse
Dicfaot-Fine
Range [M3/min]
Low
1.13
1.02
.0015
.0135
High
1.70
1.24
-.0019
.0165
(ฑ20%)
Expected
1.42
1.13
.0017
.0150
Minutes Sampled
Range [minutes] (ฑ1 hr)
All "24-hr" samples
Low
1380
Expected
1440
Hi-Vol
SSI
Dichot-Coarse
Dichot-Fine
Dichot-Total
Concentrations for Further Examination
Range (Mg/m3l
Low High
20 120
15 100
10 40
5 60
15 100
Ratio Ranges Used to Screen Data for Further Examination
Instrument Ratio
SSI/Hi-Vol TSP
Dichot(Tot)/Hi-Vol TSP
Dichot(Tot)/SSI
Coarse/Fine
Ratio Limits of Acceptance
.4 - 1.09
.4 - 1.09
.8 - 1.20
.3 - 1.30
20
-------
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-------
SECTION 4
QUALITY ASSURANCE
4.1. Introduction
Usage of the terms "Quality Assurance" and "Quality Control" varies from
discipline to discipline. For IP use, Quality Assurance (QA) is defined as
the collective efforts utilized to assure that Quality Control (QC) is properly
conducted. In general, QC is conducted at the field operator and/or in-house
technician level. QA activities verify existing QC efforts and provide or
revise QC procedures as necessary.
4.2 Quality Control and It's Relationship to Quality Assurance
Because the QC procedures are either identical or equivalent the following
discussion refers equally to TSF, SSS, and Oichotomous PM..,. and PM,., samples.
The first quality control check on the filter media is a visual inspection
(100%) to detect pinholds or other defects. If defective, the filter is
discarded. Next the weighing technician weighs the filter (Tare weight) and
records the value and filter serial number. For QC purposes, at least 4% of
each batch of filters are reweighed by a different weighing technician. The
point here is that the operators conducting the work are responsible for QC.
An external auditor conducts a weekly, unannounced, QA audit by reviewing the
logs and weighing records and selectively reweighing a small subset of the
filters prior to their being shipped to the field.
In the field, the Field Operator is responsible for QC. He verifies
that the instrument is operating properly by performing sample handling,
sampler operation, inspection/maintenance, and calibration as specified in
Section II (Instruments Operation and Maintenance) of the EP Quality Assurance
Manual11. Each time the operator operates the sampler, he is supposed to
visually inspect the sampler for damage, proper operation. Leaks, etc. He
measures and records the initial sampler flow setting and verifies and records
the sample time. Upon completion of the sample run, the Field Operator
conducts a final flow check and records both the final flow and final time on
the data card.
The operator is required to perform a one point QC calibration flow
check after each fourth sample. Flow rate adjustments are made on the basis
of this flow check to keep the sampler within tolerance. The sample time,
flowrate, and calibration flowrate data are recorded directly upon the data
card, therefore, the information is returned to EMSL, RTP with the sample.
Further, the data card provides a comments section for the operator to report
any unusual observances including equipment malfunction or unusual situations
22
-------
which may affect data accuracy. Some examples are snow/ice storms, forest
fire, or heavy construction which may elevate particulate levels; known
instrument malfunctions such as improper sample flow, and power outage which
decreased sample run time. Again the field operator "controls" the data
quality. He also records and returns sufficient information for a separate
verification of his field activities by EMSL, RTF personnel.
Each sample data card is checked, at RTF, by the Data Technician as the
sample is logged in. Sample collection time and flowrate must be within
specific limits (See Section 3.4) or the data card is diverted for detailed
evaluation. Frequently the data card is simply incomplete and the station
log sheet provides a source of information for completion. On occasion a
telephone call is made to the site/field operator to verify flowrate, start/
stop time, sample date, etc. On other occasions procedural errors are dis-
covered and corrected. The data card is also diverted if the Operator's flow
check value is out of tolerance (greater than ฑ10% of desired flow) or if the
comments indicate a requirement for investigation. The Field Operator has
the authority to declare a sample void if he/she observes an instrument
malfunction or other problems. At this point sample/data quality is controlled
primarily by the Field Operator and secondarily by the in-house, RTF Data
Technician. Data are accepted or rejected on this basis.
Field Quality Assurance Consists of an independent flow check audit
conducted by an EPA contractor. These audits were scheduled to occur "as
soon as possible" after a monitoring site became operational and annually
thereafter. In practice the schedule became one of "opportunity". Frequently,
the auditor would conduct an initial audit at one site and conduct the second
or third audit at a nearby site especially if the nearby site had a new or
inexperienced operator. The opposite is also true. Efficient use of travel
funds required minimum scheduling of distant sites and if weather, power
failure, or specific instrument malfunction prevented the auditor from
completing the audit, the opportunity was lost. In fact, some sites were
started up and closed down without ever receiving an independent QA audit.
It Ls therefore important for the reader to understand that data acceptance
or rejection was not made on the basis of QA audits but on the basis of, site
QC and in-house QC activities. The QA audits do show that the QC requirements
are effective and were usually correctly applied. In cases where the QA
audit results showed discrepancies greater than ฑ10% limit, the instrument
was operating at a low flow rate which would have been detected at the next
field operator flow check. Results of the audits are given in Appendix E .ind
are discussed more fully in Section 4.4.3.
Final weighing of the exposed filter and calculation of the mass concen-
trations have QC requirements similar to the initial weighing requirements
discussed previously.
From the outset EMSL has been concerned with Quality Assurance (QA).
Paralleling the growth of the IP Network, the QA activities have changed and
increased. While these changes are "evolutionary" rather than "revolutionary"
they are, nevertheless, very important. .Using internal and external calibra-
tions, QC flow checks, and operator training by EPA and contractor personnel,
EMSL has continually tried to improve data quality. To accomplish this,
twenty-two (22) people at RTF have been involved full or part time in training,
23
-------
calibration, data verification, and interpretation. Operating procedures
have been provided to each operating agency. Over 500 Site Operators have
been given specific, detailed instructions by EMSL personnel during the past
four years. EMSL's contractor has visited 142 sites for both maintenance,
calibration, and training. An example Training Form is given in Tables 4 and
5. The contractor's and EMSL's field calibration activity are discussed in
Section 4.3 below. External flow check audits by an external QA contractor
are discussed in Section 4.4 below. The Environmental Monitoring Division
(EMD) controls both the day-to-day operation and data collection of IP data
via field personnel. EMD controls the instrument repair, calibration and
field resupply and Internal Quality Assurance via in-house/contractor personnel.
Internal Quality Assurance therefore refers to those QA activities controlled
by EMD. External Quality Assurance refers to those QA activities controlled
by EMSL's Quality Assurance Division (QAD).
4.3 Internal Quality Assurance
EMSL in-house personnel and contractor personnel were both involved with
initial site set-up and instrument check-out. Initial instrument calibrations
were conducted at EPA before instruments were shipped to the field. Flow
checks were conducted by individual operators and verified by the EMSL (or
contractor) personnel during site visits. Subsequent QA audits were scheduled
annually but were adjusted downward because of budget (travel) limitations
and upward when additional site set-up provided the opportunity to audit/
flow-check/or calibrate a nearby existing site. Further, EMSL utilized a
contractor to supplement site visits. Instruments which failed either the
field operator flow check, EMSL or contractor flow check, or simply malfunc-
tioned were returned to EMSL, RTF for repair and replacement. Upon receipt
from the field, a defective instrument was inspected, repaired, and preventa-
tive maintenance performed. After repair, separate in-house personnel inspect
and perform a multipoint calibration on each instrument prior to shipment to
the field providing another QC opportunity. Example calibration curves are
given in Figures 7 and 8. One thousand ninety-three official instrument
calibrations were performed. Other calibrations were conducted but not
officially documented. Dates and Locations of official calibrations for TSP,
SSS, PM,- Dichotomous Sampler and PM,fl Dichotomous Sampler are given in
Appendix E.
4.4 External Quality Assurance
4.4.1 Overview
The Quality Assurance Division developed an external QA program for
the Inhalable Particulate Network. This program included the implementation
of external audits (both flow and analytical), and provisions Co give quality
assurance support to IP Network special studies. Details of the QA program
are provided in the Inhalable Particulate Network Operations and Quality
Assurance Manual issued originally in May 1980. Subsequent, updated versions
were published in July 1981, June 1982, and March 1983.ll
This section provides a summary of the flow audits provided by QAD for
the IP Network from its inception in 1979 through December 31, 1982. Actual
24
-------
e 4. OPERATOR TRAINING CHECK SHEET.
itructor should check each reference covered)
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Table 5. OPERATOR TRAINING CHECK SHEET INSTRUCTIONS.
1. This check sheet should be completed in sufficient detail to document,
by instrument, exactly whit training a specific individual received. A
separate sheet, therefore, should be completed for each individual
trained. Because training may be conducted over a time period of several
days, some individuals may receive only the first or last portion of the
overall training scheduled. Individual sheets will provide a record
which can be used for subsequent training scheduling.
2. Only the person receiving the training should complete the "Trainee
Section".
3. The instructor should complete the "Instructor Section" indicating date,
time, duration, and place of training.
4. The instructor should complete the "Operator Training Check Sheet" and
check each item covered. The trainee's signature will verify that these
subjects were in fact covered.
IP OPERATOR TRAINING CHECK SHEET
TRAINEE SECTION:
1. Name of Trainee:
2. Telephone Number:
3. What IP sites are your responsible Cor?
4. Was IP QA/O&H Manual Section 2 available to you prior to training?
Yes No
5. If your answer to 4 is NO, did the instructor provide you a copy of
Section 2? Yes No
6. Do you have a copy of the "IP Network-Quick Reference Operations Summary
Sheet" included in the IP Operating Personnel Agency Personnel letter
dated December 3, 1981? Yes No
7. Were you aware when the following information is to be sent to MD-8 at
RTF? (Indicate YES or NO)
a. Log Sheets - Monthly
b. Filters and data cards - ASAP
c. Field Data Sheets - Monthly
d. Equipment Requirements - As needed
e. Supplies Requirements - As needed
f. Flow Check Sheets - Monthly
Do you have any comments concerning training received?
INSTRUCTOR SECTION:
9. Name of Instructor:
10. Period of Training: Oate(s) Total Time (hrs)
11. Was the training objectives accomplished? Yes No
12. Reason/Comments:
26
-------
z
M
X
\
n
y.
o
_j
u.
z
111
IH
m
O.OM*
0.01ซ-
o.oซ-
0.014-
o.oit-
o.oio-
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o.ooa-
O.OO4-
o.oo*-
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INHALED PARTICULAR
DICHOTOMOUS FLOW OR]
SLOPE 0.009070
INTCPT 0.000994
C.COEF o.gasaea
NETWORK
CALIBRATION
CAL
IPO-ISO
SITE 11)4360039.
CAL IB. 8V MCK
DATE */ I*/ 83
23.1 ซr mn.
UU 'AM.C F0ป MlNrtft M
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Figure 8. Sample interpolation table for dichotomous flow orifice calibration.
27
-------
audit values are given in Appendix F. These audits provide the network with
an external assessment of the accuracy of a portion of the entire sampling
system. The precision of the network data is presented through the comparison
of the collocated data for each sampler type. See Section 5.2, Data Precision.
4.4.2 Flow Rate Performance Audits of IP Samplers
The flow rate devices used in QA auditing of samplers used in IPN
are the mass flow meters for TSP; and the dry gas meter, the bubble meter, or
a laminar flow element for the dichotomous sampler. These flow measurement
devices are referenced to a Rootsmeterฎ and a laminar flow element calibrated
by the National Bureau of Standards.
A QA auditor compares the sampler flow rate, measured with the audit
device, to that based on the sampler flow rate calibration. For Hi-Vol and
SSS this is 60 and 40 cfm, respectively. For dichotomous smaplers this is
16.7 2pm for total and coarse flow, respectively.
Audit data are evaluated on the basis of percent error:
Q - Q
% error = *-= - x 100 (1)
where: Q = sampler flow rate
QS = audit flow rate
Based on a desired accuracy for IP data, samplers with percent differences <
ฑ10% are rated as exhibiting satisfactory performance. Samplers with
differences > ฑ10% are considered to exhibit unsatisfactory performance and
require corrective action by field personnel.
These flow rate audits, initiated in the fall of 1979, have been conducted
according to the procedure documented in the Inhalable Particulate Met work
Operations and Qua 1 i ty Assurance Manual , March 1983, and the Qua I i ty Assurance
Handbook for Air Pollution Measurement Systems, Volume II , Ambient Air Specific
Methods .
Initially, beginning in the fall of 1979, each IP network site was to be
audited annually. Due to budget and/or travel restrictions, each site was
not audited each year as planned. Recently (1982-1983), however, each site
has received an annual audit and thus more data points are available for the
latest audits. Example Audit Sheets are given ฃor the Hi-Vol and SSS (Figure
9) and the Dichotomous Sampler (Figure 10).
4.4.3 Audit Results
The audit results for the nigh volume, SSS, and the dichotomous
samplers TOTAL and COARSE are shown in the form of box and whisker plots in
Figures 11 through 14, respectively. The box includes the 25th percentile,
the median, and the 75th percentile. The 25th percentile is the lower line
of the box, the median is the dotted line through the box and the 75th
percentile is the upper line of the box. The whiskers include all the other
data with the exception of "box and whisker" outliers.
28
-------
HIGH VOLUME AUDIT DATA SHEET
TIME START:
STATION:
ADDRESS:
SAMPLER NO:
CALIBRATION INFORMATION:
SLOPE ()
INTERCEPT (b)
ReF DEVICE S/N:
STANDARD
DATE:
"AUDITOR:"
"OBSERVER"
~HOTOR NO:
ACTUAL (act) ซ
b
BAROMETRIC PRESSURE (Pb):
TEMPERATURE (Tt): "
WEATHER CONDITIONS:
P1ซte
NjTief
No
PTate
IB
13
10
7
S
Audit
Manometer
Rซซding
(in H.O)
\\-M.O Pb
1 2 v
*
Audit Moซ
( *3/m
Sampler
Flo.
L-m*JmiD
Difference
(m3/min)
Percent
Difference
If no IMIS flow controller Installed, ute resistance p!ซtet.
If ปctu*l flow rates are desired use
Figure 9. High volume sampler audit data sheet
29
-------
DICHOTOHOUS SAMPLER AUDIT DATA SHEET
STATION MNE_
ADDRESS "
OATC_
TIME"
STATION SAROAO MO.
AUDITOR
WATER VAPOR CORRECT1QH (UVC)
SAMPLER MODEL
SAMPLER S/N'S
DRY GAS *TER
BUBBLE FLOW UT
EPA VN
INLET CUT SIZE
S/N
S/N
CORRECTION FACTOR (CO_
a*
T>?ฃ
Total
F1nป
Coarse
tflC'CT.
ROTAซiTIR
SIITI-C
T1MI
_JmmJ_
"S
t-
tป
VoIlT*
Ti<*
IffilR/UiT
SETTO1NT
( Unrin)
16^7
KJO
1.67
DiFFtar-CE
( L/nin)
s
Dlff.
* 10 micron dichots; all Mows to be tn actual
t Difference (set point flow - audit Horn detenninซl)(100)/(ซudit Ho- determined)
Total Flow . Volume (CFj
(Act) "
Total Flow . Volume (CQ
(Std) "Time
Coarse Flow . Volume
(Act) ~Tfซw
Coarse Flow . Volume_
(Std) "Time
Figure 10. Dichotomous sampler audit data sheet.
30
Reproduced from
best available copy.
-------
IB
10
I
-10
IS
AUDITS:
H-ZO
MEAN--0.04 (
j-5.1
MEDIAN * -0.0* pram
AUDITS:
Nป82
MEAN * -1.4
(j-7.2
MEDIAN'-1.9
AUDITS:
N*40
MEAN ' 0.8 pvcwn
cr-10.5
MEDIAN * 0.4 (MKMit
AUDITS:
N'41
MEAN = 0.6 i
(j-5.1
MEDIAN = -0.5 pwemt
20
1070
1901
1902
YEAR
Figure 11. High volume sampler flow audit accuracy, 1979 - 7982.
31
-------
18-
10 -
5-
i
10
IS
20
s -
-AUDITS: It'S
MEAN >-0.8
cr-8.4
MEDIAN*-0.7
I
AUDITS: It' M
MEAN = ILS
j-9.5
MEDIAN = 1.7
AUDITS: N - 31
v>M
MCOIAN > IS pvcwK
L
AUDITS: N -9
MEAN'-UpraM
0-7J -
MEDIAN -1.1 |
1979
19M
1911
YEAR
1912
Figure 12. Size selective sampler flow audit accuracy, 1979 - 1982.
32
-------
m
i -
210
ISO
170
ISO
130
70
50
30
10
0
I
a
-
_ _
a
-
-
-
-
_ _
a
-
-
_
a
AUDITS: N-Z4
~MEAM-ZSJ%~
MEDIAN--Z.4SK
~ ~*~ ~
_ I--J- I _
I
1070
ฃU
18
10
s
5
10
IS
20
1 1
"^ -
-r-
I
I
I
AUDITsTfl-37
MEAN-.SK
, (jป11J -*~
AUDITS: M-SO MEDIAM-4.9% ^HEป>ซl2%*
MEAN-1S% ^.; 9
ฐ'"ia* MEOIAMซ^U%
MEDIAN-1.3%
1
ISM 1501 1002
YEAR
Figure 13.-OichotomcKis sampler total flow audit accuracy, 1979 - 1982.
33
-------
200
110- -r
140
120
40
I
AUDITS: N-24
'MEAN-ซ7.8%~
0-117.1
MEDIAN-IS J%*
l
1079
20
1S
10
-10
-15
20
AUDITS: N-40
MEAN-U*
0-10.8
MEOIAN--1JK
AUDITS: N-37
MEOIAN-1^%
1001
YEAR
AUDITS: N-83
MEAN-1.4%
MEDIAN--a.6%
1002
Figure 14. Oictiotomous sampler coarse flow audit accuracy, 1979 -1982.
34
-------
97.7
88.0
The plots show the number of audits per year and the mean, median and
standard deviation for each year. Statistics for each sampler type for all
audits are given below. Outliers are included in the calculations but are
not shown on the diagrams.*
(1) High Volume Sampler
Number of audits: 177
Standard deviation: 7.5
Mean: -0.4%
Median: -1.0%
Percent of audits between ฑ20% limits:
Percent of audits between ฑ10% limits
(2) Size Selective Sampler (0-15 pm)
Number of audits: 113
Standard deviation: 8.4
Mean: -0.9%
Median: -0.3%
Percent of audits between ฑ20% limits:
Percent of audits between ฑ10% limits
(3) Dichotomous Sampler, Total Flow
Number of audits: 195
Standard deviation: 24.2
Mean: 5.2%
Median: 1.5%
Percent of audits between ฑ20% limits:
Percent of audits between ฑ10% limits:
(4) Dichotomous Sampler, Coarse Flow
Number of audits: 193
Standard deviation: 48.8
Mean: 11-3%
Median: 0.9
Percent of audits between ฑ20% limits:
Percent of audits between ฑ10% limits:
99.1
87.0
92.8
82.0
90.7
79.0
As experience was gained in both operations and auditing the IP Network,
audit values began to center more toward the zero percent error Line. This
is vividly shown in the coarse flow for the dichotomous sampler where between
1979 and 1980 the scale was reduced by a factor of ten. With the one exception
for the 1979 coarse flow audits, all of the boxes were within the ฑ10% bracket
and many within the ฑ5% lines.
*Exception - Figure 13, year 1979 - outliers are included to explain why
mean (25.3%) is much larger than median (2.45%).
35
-------
SECTION 5
DATA SUMMARY AND ASSESSMENT
This section provides assessment of the validated IP Network mass concen-
tration data collected from 4/1/79 through 12/31/82. A total of 157 routine
monitoring sites were established at various times during this period.
The routine monitoring data base includes 12,385 TSP Hi-Vol; 7,363
Size-Selective Inlet (SSS) Hi-Vol; and 11,056 Dichotomous Sampler 24-hour
measurements, collected on an every-sixth-day schedule. Because of an initial
emphasis on sites in the Philadelphia area to support other projects, a large
percentage of the total data collection is from this area. Also, note that
because of staggered sampler set up schedules and/or sampler downtime, TSP,
SSS, and Dichotomous samplers were not always operated simultaneously.
Therefore, care must be taken when comparing means of different sampler
types. The number of samples, means, standard deviation, etc., are given in
Vol. I, Appendix B.
5.1 DATA ACCURACY
The reader is reminded that there is no reference "TOTAL PARTICULATE",
"RESPIRABLE PARTICULATE", or "INHALABLE PARTICULATE" aerosol which one can
use to calibrate a particulate instrument for accuracy. The calibrations and
audits referred to previously are for flow rate only. Accuracy determinations
for particle size therefore rely upon laboratory studies conducted by equipment
manufacturers and in some cases by EPA6.
5.2 DATA PRECISION
Precision estimates were made by comparing duplicate, collocated like
instruments. Like instruments are defined as similar instruments, or dissimilar
instruments designed to do the same thing. Instruments were collocated at
selected sites and duplicate samples were taken. Data from these collocated
samplers from June 1979 through June 1982 are given in an unpublished report16
and summarized below.
In the report, both bias and precision
-------
The general formula for sample variance is:
2 . Z(y - y)2 J_[ 2 (Zy)21
.
s -
n - 1 or n-1 Zy - n (1)
for sample standard deviation:
s = fs1 (2)
for sample average (arithmetic mean) :
- =Zy. (3)
* n
for coefficient of variation
cv '
ซ>
By solving equations 1 through 4 for collocated data pairs (i.e., n = 2)
equations 2, 3, and 4 become equations 5, 6, and 7 respectively.
5.2.1 Estimation
Given a pair of measurements (y.., y~) ordered in the sense that the
instruments from which the measurements come always retain their identity as
either instrument #1 or instrument //2, the following statistics can be
calculated:
Standard deviation s =
2 1 1
(NOTE: the vertical bars indicate absolute value).
Average
= ^ + (6)
2
Coefficient of variation CV = s -{2 ' yi - y2*
Absolute D = 'yl - y2^ x 100 (8)
Percent Difference (y > y9)/2
37
-------
Sometimes the absolute value signs are removed to retain the sign (+ or
-) of the difference.
Signed Percent R = yl - y2 x 100 (9)
Difference (yl + V2^/2
This value can be divided by 2 to obtain
X = yl - y2 (10)
yl **2
Expressions (7) through (10) can easily be derived from one another
especially when y1 > 0, y > 0. (Multiplication by 100 converts value to
percent.)
e.g. CV = ft |X 1
D = {2 CV
D = 2 IX I
X = R where R = signed percent difference
2
Also, R = Ha (yl)
y2
Expressions (7) and (8) are estimators of relative dispersion.
Expressions (9) and (10) are estimators of relative bias.
5.2.2 Inference
Assume that y.. and y_ are both normally distributed around a mean M with
variance a . This characterizes the monitors during a given sampling period.
The concentrations may also vary from period to period but according to
another distribution. For example 24-hour particulate concentrations are
often characterized by a Lognormal distribution. In addition, the monitor
variability may change proportionally with levels of concentration.
Under these assumptions:
2 2
(s) is an estimate of a ,
y is an estimate of |j,
and CV is an estimate of a = T
M
38
-------
2
If y.. and yป are normally distributed around |J with variance a , and
T < 1 then
3
ฃn y and ฃn y. ~ N (ฃn|j, T )
Therefore,
R ~ N(0, 2T2)
X ~ N(0,
Given n values X.. , X_ ... X , where X is defined in equation (10), then
t = X fn = R_/n (11)
s s
x r
is distributed as a Student's -t with n-1 degrees of freedom where
X = Z_X , (12)
n
J
(13)
n (n-1)
and
S = 2s f i , ^
r x (14)
The precision of the instruments is also available since
T = s and 2) H T = s (.15)
Another way of estimating T according to ZiegLer17 Is
to average all the coefficients of variation according to
T = 1.25 ZCV (16)
n
where the 1.25 is a weighting factor for using paired data. This formula
applies to .data where CV < 20% as it is in the collocated data given in Tables
6, 7, and 8.
39
-------
TABLE 6. HI-VOL AND SSI COLLOCATED DATA COEFFICIENTS OF VARIATION
Site
010380023
341160006
397140003
010380023
030600004
061260001
333520001
341160006
397140003
Name
Hi-Vol to Hi-Vol
N. Birmingham, AL
Durham, NC
Broad St, Phila. ,
SSS to SSS HiVol
N. Birmingham, AL
N. Phoenix, AZ
Lakewood, CO
^Samples C.
Collocated Data (Mass)
37
23
PA 74
TOTAL 134
(0-15 (Jm)Collocated Data
37
29
6
Wilmuth Pump, Lacawana, NY 25
Durham, NC
Broad St, Phila. ,
27
PA 56
TOTAL 180
v. (%)a
4.67
4.67
6.00
(Mass)
7.81
7.55
8.50
6.24"
3.47
6.53
tb
1.90842
-6.60188*
5.05410*
3.56240*
1.19676
1.81929
-2.67033*
-1.87103
6 . 35084*
aC-V.(%) = T = sr
Students t for the Null Hypothesis that the true mean of R is zero.
-Significant at the 5% level; reject the Null Hypothesis.
40
-------
u- . n
C\J
o
z
UJ
u
e
a
ป *
u
a
e
rO
at
u
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S
5
oc
o
h-
LU
O
LL.
S
o
o
LU
3
U
a
a
Of
LU
*/>
a
o
z
o
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X
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1
z
a
ao
1
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* *2 2 SS
ปH m i-* ป
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2
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LLv 3*
-------
5.2.3 Data Presentation
When one compares actual measurements to a reference value or
standard, the signed value of the percent difference is normally represented
by:
Percent Difference = Measurement-Reference 1rtft ,,_->
Reference x luu u/j
When comparing two field instruments, however, neither instrument
is, in fact, a standard. A close approximation to equation (17) is:
Precent Difference = Measurement 1 - Measurement 2 Q (lg)
Average of the 2 measurements
If y. = measurement 1, and y? = measurement 2, equation 18 may
be rewritten as:
Percent Difference = (yl + y2)/2 x 100 (19)
The results of solving this equation for each pair of collocated sample
measurements is the signed percent difference, R (CV/V2). For analysis each
resultant (the signed percent difference R) was treated as a statistical
sample. The hypothesis to be tested is that the average difference (i.e.,
the relative bias) is zero over each data set.
One is reminded that the differences between a specific pair
of measurements include the combined effects of many potential differences.
Measurement differences are theoretically zero only if the following occur:
1. Ambient air is homogeneous (i.e., air is fully mixed in particle
size and chemical composition).
2. Identical air mass 1.8 presented to each instrument (i.e., no inter-
ference between instruments in which one instrument reduces the
particle concentration presented to the other instrument).
3. Instrument flow rates are identical (e.g., instruments are dependent
upon flow rate for particle separation).
4. Identical particle separation (i.e., identical percentage of each
size particle captured by Che instrument.)
5. Filter efficiency LS the same in both instruments.
6. Both instruments sampled over identical time periods.
7. Filter tare weight, final weight, and mass calculations are without
error.
43
-------
Because differences do occur in the above, even though they
may tend to cancel each other, it is important to consider both the average
percentage differences together with its standard error.
5.2.4 Data Processing
Data processing consists of:
1. Calculating the signed difference expressed as a percent (R explained
previously) for each data-pair collected at each site (i.e., Coarse
Fraction Dichot Mass collected in Birmingham, Alabama).
2. Calculating % Standard Deviation for each measurement pair.
3. Applying the Dixon Ratio to R for each data set to test for outliers.
4. Removing outliers.
5. Calculating the coefficient of variation where CV (%) = Standard Deviation
of R divided by ,/2).
6. Testing the Null Hypothesis that R=0 using the t-Test at a = .05.
7. Testing the homogeneity of variances by applying Bartlett's test to
variance of each mass measurement pair for each pollutant and measurement
method. The test showed that a pooled estimate of variance was generally
not possible. There were exceptions. These were 10 pra Sierra - fine,
coarse, and total; 15 Mป Beckman - coarse and total; 15 (am Anderson -
fine, coarse and total. It appears that for all the hi-vol data (TSP
and 15 Mm SSI) as well as manual Sierra and automatic Sierra dichotomous
data the variances are nonhomogeneous.
5.3 RESULTS
Collocated TSP (Hi-Vol) Mass Difference averages were obtained at three
IP sites (Table 6). From Table 6 one observes that TSP mass difference
average is not statistically different from zero in Birmingham, AL, yet they
are statistically different from zero in Durham, NC and Philadelphia, PA.
Based on these measurements one may conclude that there is substantial varia-
bility but little bias between the collocated values.
Similar conclusions can be drawn from collocated SSS Mass Difference
averages (Table 6) and all collocated Dichotomous Sampler data (Tables 7 and
8). Overall, the conclusions are that coefficients of variation (C.V.) are
slightly Larger for SSS than tor TSP and Dichotomous CVs are larger than SSS
CV's.
44
-------
REFERENCES
1. Lippman, Morton, "Size-Selective Health Hazard Sampling", CHAPTER H, in
Air Sampling Instruments for Evaluation of Atmospheric Contaminants, 6th
Edition, ACGIH, pp. H1-H25, 1983.
2. Air Quality Criteria for Particulate Matter and Sulfur Oxides, Volume
II, EPA-600/8-82-029b, pg. 3-30, December, 1982.
3. McFarland, A.R., and C.A. Ortiz, "Aerosol Characterization of Ambient
Particulate Samplers Used in Environmental Monitoring Studies: Progress
Report." Texas ASM University Research Foundation #3565, College Station,
TX, EPA Contract No. 68-02-2720, October, 1979.
4. Wedding, J.B. "Ambient Aerosol Sampling: History, Present Thinking,
and a Proposed Inlet for Inhalable Particulate Matter." Presented at
the 73rd Annual APCA Meeting, Montreal, Canada, June 1980.
5. International Standards Organization, Ad hoc Working Group to Technical
Committee 186-Air Quality: Size Definitions for Particle Sampling.
Am.Ind. Hyg. Assoc. J. 42:A64-A68, May, 1981.
6. U.S. Environmental Protection Agency. Ambient Air Monitoring Reference
and Equivalent Methods. Proposed Rules. Fed. Regist. 49:10454-10462,
Tuesday, March 20, 1984.
7. Vincent, J.H. and L. Armbruster, "On the Quantitative Definition of the
Inhalability of Airborn Dust", Annals of Occupational Hygiene, 24:245-246
(1981).
8. Vincent, J.H. and D. Mark, "The Basis of Dust Sampling in Occupational
Hygiene: A Critical Review", Ibid. pp. 375-390.
9. McFarland, A.R., and C.E. Rodes, "Characteristics of aerosol samplers
used in ambient air monitoring". Presented at 86th Mationai Meeting,
American Institute of Chemical Engineers, Houston, TX, April 2, 1979.
10. Rodes, C.E., "Protocol for Establishment of a Nationwide Inhalable
Particulate Network", Environmental Monitoring Systems Laboratory, U.S.
EPA, Research Triangle Park, N.C., May 15, 1979 (unpublished).
11. Inhalable Particulate Network Operations and Quality Assurance Manual,
Environmental Monitoring Systems Laboratory, U.S. EPA, Research Triangle
Park, N.C., March, 1983.
45
-------
12. "National Primary and Secondary Ambient Air Quality Standards", Federal
Register. Vol. 36, No. 84, pp. 8191-8194, April 4, 1971.
13. SAROAD USERS MANUAL, U.S. EPA, Research Triangle Park, N.C., APTD-0663,
p. 41, 1971.
14. Grubbs, F.E. and G. Beck, "Extension of Sample, Sizes, and Precentage
Points for Significance Tests of Outlying Observations." Tecfanometrics
(14)4:pp.847-854, November, 1972.
15. SAS INSTITUTE, INC., Gary, N.C.
16. Hinton, O.O., J.C. Suggs and J.M. Sune, "Summary of PM-15 Data Differences
Available from Collocated Field Samplers from June 1979 through June
1982", July, 1983 (unpublished).
17. Zeigler, R.K., "Estimators of Coefficient of Variation Using K Samples".
Technometrics (15)2: pp. 409-414, May, 1973.
46
-------
APPENDIX A
47
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ENVIRONMENTAL PROTECTION AGENCY 7
INHALABLE PARTICULATE NETWORK
IPN DATA, PERCENTILE RANK FREQUENCY DISTRIBUTIONS
VALUES IN MICROGRAMS PER CUBIC METER
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ENVIRONMENTAL PROTECTION AGENCY 38
IMHALABLE PARTICULATE NETUORK
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a
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x
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fป M3 O Kl Kl
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CM M *4 ป4
in r*> 91 r^ co C
in KI ^ e CM
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in eg .0 o- o
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co r- in r*
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CM e e> -> o- z
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CM CO Kl vf O UJ
o r- in 5
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500 CM e
co r- KI e o>
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in
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in
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0 Kl
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i
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z
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CM
a.
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e
*
h.
t>
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Kl
*
S
in
K
Kl
*
in
4
e
e
*
N
C>
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e
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in
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o
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in
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in
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T
Kl
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Kl
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0 jป
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e KI
CM -4
0- CO
2- JX
in ป
in ป
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e o
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Kl O
KI m
f>
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CM -^
CM ซO
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o -^
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fป CM
in KI
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in e
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CM -4
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t- H- in o
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a o u. u.
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0
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in
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Z
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in
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o
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O
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2
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C
c
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0
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in
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Kl
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COARSE 15 6(
COARSEIO (
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in
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j
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j
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4
1
in
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a.
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a.
w-
0.
SAMPLER ^
O O 0 CM
0 *n CO
* Kl co o
-o o o in
CMOO in
-ซ >o o- CM
ป in KI in
CM -* -^
0ป ^ 0* -.
Ift 1*1 <0 o in eg
in o o o
i^ ro >x r*ป
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r* in ซ CM
o in in o
CM CM m
m <* KI -*
>0 0) 0 0
rป- %r o CT-
tf O 9- O
in o
ป H- in o
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> *H O O Z Z
t-t in -< MI ป-t I-H
X OT O O U. U.
o
o
h-
X
-o
in
Kl
Kt
in
Kl
o
CM
CM
0
r-
o
in
CO
CM
-o
in
o
*o
Kl
in
0
in
o
CM
0
O
CM
O
in
o
Kl
*0
r*.
oo
COARSE15 <
COARSEIO
D2
X
Q
a.
a_
99
-------
o o -a CM
1
er. e CM
o o> -o
ro o o
ro 03 ป
a in t>.
CM CM r*ป CM e
ro CM M - ซj
UJ
f e r> co
CM CM a -"
CM CM * O
ซO -a- ro ซ
s
CM CO -O
f^ in 10
o in
CM -
m a:
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Z 0.
O
i e -o CM
f* r*ป
O CM i
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a
e in -7 co
o -5- 03 o
_i co -o rป
CM
CO
e r* e r> o
M e -o rป
* -o o o-
- ,0 ซ CO
flป in o
f^ CM CM O
O
in
ro ซ) CM to
-i ro co CM
CM -o o in
^ CO O* O
49
in
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10 m
r*. in -J-
CM
eg
> r uj in
z a ป *" a a.
uj p a u >-
< t- >- S i
ui u D
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UJ r^
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r* H- O uj -J o
U ^ UJ Qp UJ QB
LJ -i a 03
t- D u. in u
o u i: ui
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< o. a t^
r- uj u Q.
Z UI -i M K
UJ -J HI C O
CM CM -"
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CM o m
e in e
o CM o
f o- o
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N. I
CO I
CM
ro
CM
CM
e
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t*.
CM
: z z CM
o
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a < u
M x cr in o in
> z uj uj n
M a.
in
in ro CM -*
o o o
000
O> 10 ซJ
in -o o
o
o
vO
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in in o o
f^ fO CO CM
ป o in >*
r a- m o
CM
O
a.
z
or
iu
_j
a.
r
in
a ป 03
<ซ CM
^ O IO O *O I
ซO CM ~O -O
in o
H ฃ in i
J o o -
o x x uj i
> M u u z :
M tf> ป* >H W I
x m o o u. i
rป
e
CM
i in in
i ex a:
: < <
i o O
. u u
CM O
in -T
o in o
in rป o
to I**, o
in ...
CM ^ rO CM
o. in ro ro
o
o
a> ro
* -r co
-T CM CM
f -a o
*r in *o
^ ro
O
rx
e
o) in o ro M
-i r* ro * ซ
0x0
Bk ro ซ ซ^
co o o o o o o
CM ro ro ro
in '
ui o
-i -i O O - in in
a. o xxiuuao:
r >MUUZZ<<
< MtflMMMMOO
m xinoou.ii.ou
100
-------
APPENDIX C
101
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT1S/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FIKE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
80
38
0
0
0
0
0
0
0
0
N
178
146
147
147
147
136
41
41
41
40
N
40
38
89
89
89
33
0
0
0
0
aj.it = uiujo
MEAN
74.2151
61 . 1068
.
f
f
f
.
,
f
W U U 3 M W /
STD
36.0512
17.4928
.
.
f
f
.
.
f
ITE=010380023A07 NAME
MEAN
109.613
84.313
57.914
28.675
29.236
0.557
53.247
30.410
22.838
0.515
SITE=01038002
MEAN
1 16.739
86.909
64.430
28.989
35.442
0.632
f
t
.
.
STD
63.4217
43.0757
32.2247
13.5179
22.601 1
0. 1263
35.4951
17.2730
20.3282
0. 1208
nflnt-^u
MIN
20.95
25. 19
.
.
,
.
.
,
m
=NORTH
MIN
25. 9200
27.7200
13.3900
6.8900
2.8600
0. 1554
15.7100
7.7800
4.5300
0.2854
3A57 NAME=NORTH
STD
61 .7199
43.7502
36.8960
14. 1894
27. 3802
0.0912
.
.
.
m
MIN
37.2900
29 . 1200
18.4300
7.9300
1 .0000
0.4987
,
.
.
f
uin sj.Knj.nvin
MAX
242. 10
93.52
.
.
f
f
,
.
f
BIRMINGHAM (
MAX
368. 600
238.200
182.300
73.900
125. 100
0.848
172.500
79.800
100.000
0.939
BIRMINGHAM
MAX
276.000
205.200
187.800
71 . 500
147 .200
0.879
.
.
.
t
STARTED
790801
810323
,
t
.
t
f
.
S*> t\ T 11 >
Z OTH 1 ~~
STARTED
790708
800421
790708
790708
790708
.
820324
820324
820324
COL
STARTED
810317
810311
810323
810323
810323
.
.
.
.
.
END_DAT
810317
81 1 124
.
.
.
.
.
END_DATE
821231
821231
821231
821231
82 1231
.
821231
821231
821231
END_DATE
811218
811124
821231
821231
821231
.
.
.
ซ.
.
102
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
74
32
0
0
0
0
0
a
0
0
N
89
90
84
84
84
82
0
0
0
0
O J
N
0
0
60
60
60
0
0
0
0
0
MEAN STD MIN MAX STARTED
97.9834 53.1816 25.74 306.3 790726
65.5609 27.0276 24.22 141.9 810516
. ซ...
. ...
. ... .
. * . .
....
* ....
. . .
.
MEAN STD MIN MAX STARTED
60.1009 19.8754 20.7900 132.800 800503
49.0081 15.3273 19.3300 95.940 800503
43.0185 18.3638 12.9200 95.190 800509
23.6720 9.8021 6.6100 51.460 800509
19.3462 12.6506 3.2900 58.140 800509
0.7050 0.1954 0.3767 1.544
. . .
... . .
... . .
r T P * rt 1 ^^OrtrtOQH ft ^ \t H M F " M rt O T T V ft ?!/* & f* C* 1* H 1* rt 1 f I* O ^
LTE- U 1 Z 38 0 0 Z y AU / NAPIE-nOBILE IWKRG STA TOWER;
MEAN STD MIN MAX STARTED
ซ...
39.2513 16.2769 16.45 86.05 810907
20.3378 10.0071 6.58 47.57 810907
18.9138 10.5015 5.18 56.88 810907
.
....
.
.
END_DATE
810510
81 1 124
.
.
.
.
.
.
END_DATE
811031
81 1031
81 1031
811031
811031
,
,
.
.
END_DATE
.
821231
821231
821231
.
.
.
.
103
APPENDIX C
-------
ENVIRONMENTAL PROTECTIOM AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATI015 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COAP.SE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
116
4 1
82
82
82
68
0
0
0
0
N
146
96
95
95
95
90
49
49
49
47
N
71
75
50
50
50
0
0
0
0
0
SJ.Tฃ. = UOU><
MEAN
41 . 3222
30.9524
23.9704
7.3344
16.6365
0.5035
,
^
B
MEAN
1 14.879
80.294
66.479
24. 158
42. 322
0.584
39. 229
15. 264
23.965
0. 383
MEAN
110. 158
74.795
53.652
15. 852
37.799
.
.
.
.
.
I4UUUD AU /
STD
17.7390
12. 1812
1 1 .2229
3.0555
9.8213
0. 1008
.
m
f
^ A > n rt *? vr a
i U & A U / MA
STD
43.5056
32.5482
30.8640
18.0797
19.5586
0. 1839
17.8777
9.7582
1 1 . 1009
0.0823
9AฃnftAflllllftv7
JUOUUUUHAU /
STD
43.0318
28.8708
21 .2844
8.7184
17.0454
.
.
.
.
.
MAnE. = <-AKl
MIN
10.2400
10.8900
3.4030
1 .2080
1 .6250
0.2684
f
f
f
n t * tt u ฃ* r\ ฑ f
MIN
28.8800
22.5500
12.3900
6.0900
5.5800
0.2995
12.8100
5.5300
3.2300
0. 1899
MIN
24.78
28. 17
14.06
4.86
5.65
.
.
.
.
.
-r Ktr. AJ.KMJK
MAX
98. 2600
67.6400
68. 1700
16.5500
57.4900
0.8563
.
f
t
(Q/\/\C"TปtFTปT H*
KUU5E VELT
MAX
270.900
179. 100
148.400
106.900
106.000
1 .528
99.540
66.910
51 . 340
0.577
^ D 1* U DUnC* Vf T V
JKTH rnUtnlX
MAX
239.3
155.7
112.9
37.0
75.9
.
.
.
.
,
i
STARTED
790813
801205
810504
810504
810504
.
.
t
t
*ซ wm \
STARTED
790831
800720
801223
801223
801223
.
820129
820129
820129
STARTED
790813
800316
810603
8 10603
810603
.
.
.
.
.
END_DATE
821014
81 1 130
82 1014
821014
821014
.
.
.
.
END_DATE
821231
821231
821225
821225
821225
821225
82 1225
82 1225
END_DATE
810504
81 1 124
82051 1
82051 1
82051 1
.
.
.
.
104
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATIO 15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
0
24
0
0
0
0
0
0
0
0
N
1 14
63
32
32
32
31
0
0
0
0
N
1 13
68
92
92
92
52
0
0
0
0
ij. ir.-ujvouu
MEAN
70.8133
MEAN
62.
52.
34.
18.
16.
0.
.
.
3267
2378
9144
6606
2537
5791
- SITE=05050
MEAN
126
98
57
28
28
0
.717
.41 1
. 189
.765
.426
.535
f
.
.
.
U UHA3 /
STD
26.6832
STD
22.4546
19. 1933
13. 4013
8.5927
6.9797
0. 1 194
,
.
.
0002A07
STD
49. 9182
41 .7206
39.8249
19. 1999
31 . 9222
0. 1988
r
f
r
.
nAiii.- nun a. n rnur.ซxA
MIN MAX
38.61 127.7
MIN
27.
20.
10.
5.
3.
0.
.
.
.
HMIIC. - i, j. A i Ait, nui
MAX
6500
3000
0400
0600
8400
3109
NAME=AZUSA
MIN
20.
15.
3.
2.
1 .
0.
B
.
m
.
3500
8800
8450
0240
0000
2148
133
124
69
41
32
0
.900
. 100
.320
. 100
.820
.829
f
t
(LOREN
MAX
273
216
303
90
283
1
. 600
. 300
. 600
.800
.600
. 312
.
f
,
STARTED
810703
" V ซ _ _ _
ปK
STARTED
801 129
801 123
820523
820523
820523
,
.
.
m
H \1 V \
A V JL ; ___ .
STARTED
790813
790813
791018
79 10 18
791018
t
.
END_DATE
811124
END
82
81
82
82
82
END
81
81
82
82
82
_DATE
1231
1212
1207
1207
1207
.
.
.
f
_DATE
0925
1 1 18
1 107
1 107
1 107
.
f
.
105
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE 10
RATIO 10
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
84
33
126
126
126
83
0
0
0
0
N
92
92
5
5
5
0
0
0
0
0
N
85
49
1 1
1 1
1 1
0
0
0
0
0
axit=u
MEAN
51 .5505
44.6270
28.0009
19.0584
8.9423
0.5630
.
.
,
SITE=0 13200
MEAN
120. 169
84.368
29.294
14.890
14.404
.
.
.
.
AAfiAAAoi
ZOO'tUUU^J
STD
47.2029
27. 1213
27.6299
3.8746
26.7941
B
.
.
.
.
LU / nAnt =
MIN
12. 1600
24.0500
8.7020
4.7460
0.6700
0.3272
.
.
f
nxn BKUUK
MAX
138.400
73. 140
64.650
51 .040
41 .240
1 .055
.
.
B
NAME=TARRANT (PINSON
MIN
28.74
22. 10
18.26
7.58
10.59
.
.
.
.
nn*7 u ii M v
\\j / nAPlE-
MIN
5.321
8.263
7. 156
2.590
1.121
.
,
.
*
.
MAX
324.60
173.50
45.32
29 .78
19.10
.
.
.
.
\j /^ U rt D H f* V
ANCHORAut.
MAX
260. 30
118.40
103.10
15.68
92.70
.
.
.
.
.
STARTED
790726
810516
790726
790726
790726
.
.
.
,
ST
STARTED
790720
800421
821201
821201
821201
.
.
.
.
STARTED
800831
800831
821002
821002
821002
.
.
.
.
.
END_DATE
810510
81 1 124
820312
820312
820312
.
.
.
,
END_DATI
810516
811124
821231
82 1231
821231
.
.
END_DA'Ti
820722
811118
821231
821231
821231
.
106
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
116
41
82
82
82
68
0
0
0
0
N
146
96
95
95
95
90
49
49
49
47
N
71
75
50
50
50
0
0
0
0
0
5ITE=Wi
MEAN
41 .3222
30.9524
23.9704
7.3344
16.6365
0.5035
.
.
,
SITE=03060
MEAN
1 14.879
80.294
66.479
24. 158
42. 322
0.584
39.229
15.264
23.965
0.383
MEAN
110. 158
74.795
53.652
15.852
37.799
.
.
.
.
f
U44UUUDAU /
STD
17.7390
12. 1812
1 1 .2229
3.0555
9.8213
0. 1008
.
.
.
MAnt=UA
MIN
10.2400
10.8900
3.4030
1 .2080
1 .6250
0.2684
.
.
.
Ktr Ktt AXK^UK
MAX
98.2600
67. 6400
68. 1700
16.5500
57.4900
0.8563
.
.
.
0002A07 NAME=PHOENIX (ROOSEVELT
STD
43.5056
32.5482
30.8640
18.0797
19.5586
0. 1839
17.8777
9.7582
1 1 . 1009
0.0823
STD
43.0318
28.8708
21 .2844
8.7184
17.0454
.
9
.
.
.
MIN
28.8800
22.5500
12.3900
6.0900
5.5800
0.2995
12.8100
5.5300
3.2300
0. 1899
\i ft M r*
A AH ฃ.
MIN
24.78
28. 17
14.06
4.86
5.65
.
.
.
.
f
MAX
270.900
179. 100
148. 400
106.900
106.000
1 .528
99.540
66.910
51 .340
0.577
VfAD'PU OUrtfVTV
nuKin r n u & xt x A
MAX
239.3
155.7
112.9
37.0
75.9
B
.
f
m
.
i
STARTED
790813
801205
810504
810504
810504
.
.
.
.
'
C* ip \
3T > -
STARTED
790831
800720
801223
801223
801223
.
820129
820129
820129
STARTED
790813
800316
810603
810603
810603
.
t
t
f
.
END_DATE
821014
81 1 130
821014
821014
821014
.
.
.
.
END_DATE
821231
821231
821225
82 1225
821225
821225
821225
821225
END_DATE
810504
811124
82051 1
82051 1
82051 1
.
f
.
.
.
107
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOTIS/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
0
24
0
0
0
0
0
0
0
0
N
1 14
63
32
32
32
31
0
0
0
0
N
1 13
68
92
92
92
52
0
0
0
0
axrt=uauou
MEAN
.
70.8133
.
.
.
,
.
.
.
MEAN
62.3267
52.2378
34.9144
18.6606
16.2537
0.5791
.
.
.
UUUHA3 /
STD
26.6832
.
,
^
f
.
.
f
Idiinnninn
4HUUU 1AU
STD
22.4546
19. 1933
13.4013
8.5927
6.9797
0. 1 194
.
.
ป
SITE=050500002A07
MEAN
126.717
98.41 1
57. 189
28.765
28.426
0.535
.
.
.
f
STD
49.9182
41 .7206
39.8249
19. 1999
31 .9222
0. 1988
.
.
.
f
NAnt = NUKa.
MIN
38.61
.
f
.
.
f
^
.
*7 U It M C*
7 NAME-
MIN
27.6500
20.3000
10.0400
5.0600
3.8400
0.3109
.
,
.
n rnut.nj.% 1.1
MAX
127.7
.
.
.
.
9
f
.
T T'PI'T V Drt^L*
LITTLE ROCK
MAX
133.900
124. 100
69.320
41.100
32.820
0.829
.
.
.
NAME=AZUSA (LOREN A'
MIN
20.3500
15.8800
3.8450
2.0240
1 .0000
0.2148
.
.
.
f
MAX
273.600
216.300
303. 600
90.800
283.600
1 .312
.
.
.
.
;ut;
STARTED
810703
,
.
.
.
f
t
.
'
STARTED
801 129
801 123
820523
820523
820523
.
ป
,
.
STARTED
790813
790813
791018
791018
791018
.
.
.
.
.
END_DATE
81 1 124
.
.
.
.
'
END_DATE
82 I 231
811212
821207
821207
821207
.
.
.
.
END_DATE
810925
811118
82 1 107
821107
821 107
.
.
.
.
108
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
si.
N
61
40
53
53
53
40
5
5
5
3
N
1 16
49
25
25
25
23
0
0
0
0
h
N
58
0
66
66
66
51
0
0
0
0
rt = U3US2UUOHAU / HUtlC. = fl AKฃ.Kฃ>T J..L.LLI ll*n&:>IC.K A V i >
MEAN STD MIN MAX STARTED
123.285
1 13.370
64.036
30.803
33.224
0.552
69.550
49.524
20. 026
0.550
._ ____ .^ ^ j
MEAN
57.0921
47.7724
27.6988
9.9920
17.7064
0.5236
.
.
f
!,<
MEAN
57.6379
.
39.4053
19.8732
19.5286
0.6190 .
.
. .
.
^
56. 1972
56. 1752
38.9251
29. 1900
18.5061
0. 1644
8.2054
6.2518
3.4830
0.0421
STD
26.3039
25.6639
1 1 .9557
4.0733
9.3564
0.0719
,
.
,
^ rt ft O * ft *7
} U U 6 A U /
STD
19.9620
.
19.3135
13.9289
12.4189
0.0876
.
.
.
f
40.8400
27.0800
14.5500
7.4300
5.5100
0.3312
57.6700
43. 1400
14.5300
0.5130
A <7 n /\ *7 vr
0 i AU / n
MIN
16. 1600
12.9000
10.5300
4.6400
3. 1600
0.3654
.
.
xซ
MIN
13.2700
.
7.3780
4.9900
1 .9770
0.3712
.
r
f
.
356.000
372.200
195. 100
140.800
1 10.400
0.991
79.920
58.480
24.000
0.596
MAX
176.500
147.800
47.360
24.220
34.340
0. 644
.
.
f
^TT*f*rt /T*T
DIEGO ( EL
MAX
99.580
f
1 13.500
92 . 300
76.500
0.891
9
f
B
.
800924
800918
801 1 17
801 1 17
801 1 17
.
821207
821207
821207
STARTED
800831
800912
820324
820324
820324
m
.
,
.
ft ซ T f\ \T \
CA JON )
STARTED
811218
.
810925
810925
810925
.
.
.
.
END_DATE
821231
810907
821201
821201
821201
.
821231
821231
821231
'
END_DATE
821231
81 1 130
820815
820815
820815
.
.
.
"
END_DATE
821231
821231
821231
821231
.
.
.
109
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUmiARY
RATI015 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
v
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15 .
RATI015
DICHOT10
FINE VO
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATIO 10
N
64
52
2
2
2
0
1
1
1
0
N
84
88
153
153
153
73
0
0
0
0
C T T I!"
N
52
0
58
58
58
48
0
0
0
0
&X1 t=U3^
MEAN
117.759
100.769
42.060
10.315
31 .745
.
47.900
35.050
12.850
MEAN
86.4383
71 . 1741
40.9786
18.4784
22.5012
0.5444
,
f
,
MEAN
77. 6740
.
45. 0462
17. 3978
27 .6483
0.5463
.
.
m
BUUUU3AU /
STD
50. 1014
52.2639
7.2408
0.7283
6.5125
.
.
.
.
AC^o^ftftn^nn*?
U3&O6UUU&AU /
STD
66. 1273
50.6819
30.9271
17.5346
23.1011
0.3027
,
.
ft ^ H rt *7 If M M r*
U & A U / NAn t
STD
41.7611
.
27.2728
15.5469
19 .3722
0. 1505
.
.
.
,
jtAnt = r Kt
MIN
24.73
17.64
36.94
9.80
27. 14
.
47.90
35.05
12.85
\t n Mr*
NAnE-
MIN
4.49000
3.96700
2.28200
1 .00200
0. 13000
0. 16743
,
.
.
MIN
18.5900
,
8.0380
2.2400
4 .7540
0. 1696
.
.
.
f
SrtU V t U^XVJ
MAX
262.60
254. 00
47. 18
10.83
36.35
.
47.90
35.05
12.85
^ T XT f B f\ T Vf T C?
FIVE POINTS
MAX
307.800
253.500
218.900
98.500
145.300
1 .465
,
,
.
MAX
233.700
.
138.800
62 . 630
125.700
1.019
,
.
.
9
i ;
STARTED
800825
800825
820914
820914
820914
.
821207
821207
821207
STARTED
790930
800209
790930
790930
790930
.
.
.
.
STARTED
790924
.
790924
790924
790924
.
.
.
.
.
END_DA1
8202H
81 1 1 If
82092C
82092C
82092C
.
82120"
82120"
82120";
END_DATE
810510
81 1025
821020
82 1020
82 1020
.
,
END_DATE
801217
.
80 1217
80 1217
80 1217
.
.
.
.
110
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATI015 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
.RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
a j. .
N
1 1
2
82
82
82
10
0
0
0
0
N
126
60
91
91
91
77
0
0
0
0
N
77
95
147
147
147
69
0
0
0
0
Li=V3HUฃUVV
MEAN
52
69
30
12
18
0
. 1745
.8550
.5166
.2595
.2577
.5116
.
.
.
" ~ O J. i. L.
MEAN
64
43
36
10
25
0
.4717
.6602
.0798
.6314
.4486
.5678
.
,
.
JAW/
STD
14.
18.
14.
8.
1 1 .
0.
.
.
.
STD
19.
15.
12.
4.
1 1 .
0.
.
.
ni
3394
5333
1457
6539
1382
1284
f\ ft f\ f\ f
U O U U I
4104
4183
4420
6488
1804
0910
CTTP ftCtl1<*rt1ft^1lrt^
o X I ฃ U 3 4 1
MEAN
78.7738
67
46
26
19
0
.8715
.5464
.7518
.7947
.647 1
.
.
.
.
O V 1 V
STD
30.
23.
20.
18.
8.
0.
.
.
.
.
J ซ U /
2078
8499
9216
6665
6847
1767
U 1 ฃ. - ii J.
MIN
37.
56.
8.
3.
3.
0.
.
.
.
\ ? H f\7
i (* A U /
MIN
15.
15.
9.
3.
3.
0.
.
.
.
V mil UK
2500
7500
3200
4200
5330
3659
VT H M r*
I\Arlฃ*
5000
3000
1550
2700
0860
4022
UBMf 1 1 F C T
ft Ant. - WLb i
MIN
31 .8300
18.
14.
5.
1 .
0.
.
.
.
.
0400
2400
3300
0000
3446
ฃ. ซ. <->
MAX
83.
82.
89.
63.
76.
0.
.
.
.
ฑU I XI
0300
9600
3700
6600
0700
8031
tii i a i i
STARTED
810329
810603
810329
810329
810329
.
.
.
.
END_DATE
810528
810627
82082 1
82082 1
82082 1
.
,
t
f
T r\ M D n f*
MAX
109
81
64
30
56
0
T f\ &
LUb
MAX
167
154
165
156
59
1
.800
.940
.730
. 150
.640
.928
.
.
,
X \i f* r* T
ANGEI
.700
.000
.000
. 900
.290
. 124
B
B
B
.
STARTED
800813
800813
810329
810329
810329
.
.
.
>
1 ^ f9
,ES
STARTED
790708
800215
790708
790708
790708
,
.
.
.
END_DATE
821231
810826
821231
821231
821231
.
f
END_DATE
810227
811118
821014
821014
821014
,
.
.
111
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
IHHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
76
89
28
28
28
12
0
0
0
0
axit=
MEAN
98
74
58
34
24
0
.2570
. 1772
.8882
. 1743
.7143
.7456
.
.
.
.
uso i a UUUHAU / NAnr.=
STD MIN
38
27
24
16
13
0
.2147
. 1999
.8345
.8566
.4513
. 1765
.
.
,
.
26
18
16
9
6
0
.0400
.7600
.6700
. 1600
.7300
.3955
f
.
B
.
:fAoAUtNA
MAX
239.
156.
1 17.
75.
61 .
1 .
.
f
t
.
300
000
400
400
200
072
STARTED
7907
8001
7910
7910
79 10
14
22
18
18
18
.
.
.
f
.
END_DATE
8
8
8
8
8
10516
1 1 130
11212
11212
1 1212
.
.
.
.
t
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FIME10
COARSE10
RATI010
N
88
76
167
167
167
75
0
0
0
0
a X 1 t. = I
MEAN
54
41
28
13
14
0
.8750
.2408
.3060
.9197
.3864
.5370
. /
/
/
Joo.suuuu.3AU/ NAni = Kxi;nnuriiJ UA
STD
20
19
14
1 1
7
0
.0637
. 1956
. 1891
.3327
.4735
. 1898
.
.
.
t
MIN
24
15
7
3
1
0
.8100
.0600
.8850
.2170
.9300
.2413
f
.
.
f
MAX
130
118
98
76
41
1
.000
.400
.470
.850
.640
.259
,
.
.
f
STARTED
790924
800304
790924
790924
790924
.
.
.
.
f
END_DATE
81051
81072
82101
82 10 1
82101
6
1
4
4
4
.
f
.
,
f
oX i t = U 3D 3 i3U U 1 AU / H Ant = KU H J.UU U A IHXooXUf
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
129
128
127
127
127
89
47
47
47
42
MEAN
148.
121 .
98.
43.
55.
0.
76.
43.
33.
0.
024
691
427
337
087
693
646
1 1 1
531
570
STD
75
64
46
28
27
0
35
28
16
0
.9261
. 1864
.9345
.6691
.8492
. 1180
.8944
.4797
.6410
. 1490
MIN
18
10
14
1
3
0
16
4
5
0
. 1700
.3600
.0300
.8200
.5700
.4539
.8100
. 1600
.8800
.3702
MAX
464
387
267
163
125
1
199
154
62
1
.800
.200
.600
.800
.800
.071
. 100
.700
.360
.268
i Bi. VLI 1
STARTED
790825
800316
790819
790819
790819
.
820204
820204
820204
.
END_DATE
82
82
82
82
82
82
82
82
1231
1231
1231
1231
1231
.
1231
1231
1231
.
112
APPENDIX C
-------
RATIO 15
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
DICHOT15/HI VOL RATIO 1 0 = DICHOT 1 0/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
1 12
0
1 15
1 15
1 15
103
0
0
0
0
N
100
10
174
174
174
90
0
0
0
0
N
104
57
4
4
4
3
0
0
0
0
5JLiE = ui>oeou
MEAN
58.7240
.
31 .3246
16.3522
14.9725
0.5304
.
.
.
MEAN
87.5341
62.7570
38.5684
17 .7884
20 .7786
0 . 4787
.
.
.
Tป r A&nnfinrtn
TZ.-UOUUBUUU
MEAN
37.2538
28.5635
13.2717
5. 4420
7.8297
0.5988
.
.
.
m
UU4AU /
STD
25.2010
.
17.0434
12.6762
8.2520
0. 1451
ซ
.
.
cฃQonftntin
OO7OUUU4A
STD
44.7166
9.0441
20.7284
16.4867
9.2942
0.1413
,
.
.
ซAnt=SAn i
MIN
23.200
.
9.234
3.580
1 .330
0. 154
.
.
.
ft *7 v R M r -
U / A AH t, -
MIN
20.9300
52.6900
10.6600
3.7200
4.5200
0.2885
,
.
.
o * ft "7 MUMP T%rI\M7rlt5
oAU/ NAnt-DLNVLR
STD MIN
16.8759 6.54400
10. 6650
3.6535
0.6721
3.5103
0. 1436
.
.
,
f
9. 16100
8. 14700
4.84800
3.29900
0 . 43544
.
.
.
m
' KAJXUJLฃ>UU
MAX
165.600
.
1 12. 300
75.500
48.880
1.116
.
.
.
MAX
262.50
85. 13
122.60
111.60
52.68
1 . 00
.
(QlT^lr'T T"V
BUCKLEY
MAX
107.700
51 .720
15.940
6 . 300
10.970
0.705
t
,
STARTED
791 1 16
.
791122
791 122
791 122
.
.
,
.
STARTED
790930
810603
790930
790930
790930
.
,
.
.
T* ^ T* T ** \
FIELD J
STARTED
800714
8007 14
821101
821101
821101
.
f
f
t
.
END_DATE
820914
.
820914
820914
820914
.
.
.
.
END_DATE
810528
810727
821014
821014
821014
.
.
END_DATE
821207
811031
821207
82 1207
821207
.
.
.
,
113
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
132
76
10
10
10
10
0
0
0
0
N
67
37
27
27
27
25
0
0
0
0
N
0
15
27
27
27
0
0
0
0
0
aฑiL,- VO UOO
MEAN
102.596
70.608
55.535
18.884
36.651
0.504
f
,
MEAN
66.0773
49.8438
33.0752
1 1 .2352
21 .8404
0.5204
.
.
.
Y v u i AW / n
STD
46.7513
35.9391
20.6897
9.2774
16.2108
0.1114
.
.
.
260001A07
STD
36.2274
25.2766
15.3134
8.7104
10.4447
0.0913
.
.
Rilf.-UL.nVC.lf.
MIN
14.4200
27.5800
20.7400
8.9000
1 1 .8400
0.3907
.
f
,
v 1 1 J. n z> i K.C
MAX
284.600
235.600
88.580
41.010
66.910
0.754
t
f
.
NAME=DENVER (LAKEWOC
MIN
26.9200
19.8700
16.9900
3.2800
7.3000
0.3533
,
.
CTTTT7 ftA1^Aftftft1HC*7 vr ป iyปT* t%T^vrtTC"ซ
oXlt-UDl^DUDUlAi)/ Jl
MEAN STD
40.2333
33.7644
12.31 15
21 .4541
.
,
.
.
.
13.8200
21 . 4184
9.8586
14.5678
.
.
.
.
.
Hiir. uc.nv E.K
MIN
23.48
14.22
3.41
4.85
.
.
.
.
.
MAX
258.80
140.50
72.38
44.89
52.49
0.70
.
.
(T II T/ T? Y T f^ r* n
L AKC.WUUU
MAX
77 .84
97. 42
41 .88
56.68
.
.
.
.
.
STARTED
800714
800714
820622
820622
820622
.
.
.
.
ป T% %
JJJ ) _ __.
STARTED
800720
800720
810721
810721
810721
,
.
.
STARTED
810727
810727
810727
810727
.
.
.
.
,
END_DATE
821219
811218
821207
821207
821207
.
.
.
.
END_DA"
8206 1-
810911
82061s
8206 !'
82061i
END_DATE
81 1 130
820616
8206 16
820616
^
.
.
APPENDIX C
114
-------
ENVIROHMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
ปJ
N
2
12
8
8
8
0
5
5
5
2
N
63
19
25
25
25
15
0
0
0
0
N
98
94
139
139
139
93
0
0
0
0
L 1 i = U O I81UUI
MEAN
83
59
26
1 1
15
34
17
17
0
.4300
.7092
.5312
.5037
. 0287
.
.5460
.0520
.4920
.4632
MEAN
25.9420
18
43
13
29
1
< T*rr
.0846
.2368
.2876
.9484
.0776
.
.
Oj. 1 L - U / V Ti 1.
MEAN
60.1315
45
33
18
14
0
.3822
.3637
.3949
.9686
.5352
.
.
.
.
1 1 AU /
STD
40.
28.
10.
2.
10.
.
15.
9.
7.
0.
STD
13.
10.
38.
12.
33.
0.
.
,
,
\AAOK
l(J(J3f\
STD
26.
21 .
16.
10.
8.
0.
,
.
,
,
jiAnr.-rui.i3.Lu i
MIN
8283
3377
6679
0421
9545
7045
3398
3613
0734
3776
4793
2665
8662
2007
4135
m i
u / 1
6885
0856
3647
991 1
2470
1085
54
22
15
9
2
18
8
7
0
7
/
5
6
13
4
3
0
4 A M F
.5600
.2500
.4000
.3000
.0200
.
.9700
.4600
.0700
.4113
\t H M r* V t
MAne. - 1 1
MIN
. 1790
.5640
.5200
.3400
.6300
.4341
.
.
f
MIN
16.2100
9
10
4
2
0
.7290
.9000
.2900
.2600
.3555
^
f
9
^
i ur.rt i K
MAX
1 12.
102.
44.
14.
35.
.
57.
32.
25.
0.
\ D rp /ป f\
A.L ni
300
000
580
960
170
840
530
310
515
T T T \r t
JK1 UUiiiixn;
MAX
65.640
43.
208.
46.
175.
2.
f
.
.
MAX
199.
144.
120.
58.
61 .
0.
.
f
.
.
960
400
420
800
029
IT D T T f
UBLIC
500
500
300
600
600
971
STARTED
821225
810721
81 1025
81 1025
81 1025
821207
821207
821207
5 _____
STARTED
810215
810311
82051 1
82051 1
82051 1
,
m
m
.
* T TT B ^
STARTED
800 1 10
8001 10
800203
800203
800203
.
.
END_DATE
821231
811218
821 1 19
821 1 19
821 1 19
t
821231
821231
821231
END_DATE
821231
810715
821213
82 1213
821213
,
.
.
END_DATE
81 1 130
811130
820622
820622
820622
.
.
.
115
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATIO 10
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
70
0
54
54
54
40
0
0
0
0
N
50
0
80
80
80
34
0
0
0
0
C T
b J.
N
1 18
75
35
35
35
26
0
0
0
0
ii, = i;/uf/ou<
MEAN
33.0549
r
19.0769
1 1 .6502
7.4277
0.4911
.
.
,
J 1 H.
END_DA'.
810711
81 123T
81123,
81123
T*rป rtOrt1Onnrt1llrt*' IT ซป*ซ itTTiytTvr **ซ** ปr -nr* f/tTjiirM/xปrซป'%
i ฃ v o v i o v u
MEAN
51 .7469
41 .7167
33.4034
20.3743
13.0300
0.6204
f
.
.
.
v irtu/ nttiit w j-iiiixnu x un Lie. i ^J-i
STD MIN MAX
17.9857 20.9400 107.900
15. 1 144
13.2490
10.1231
6.3696
0.0953
f
.
.
.
13.0700
12 . 6700
6.7200
4.5300
0.4718
a
.
.
.
84.810
67. 980
48.230
29. 120
0.809
,
.
.
.
Airiurti^
STARTED
800912
8009 18
820405
820405
820405
.
.
.
.
.
END_DATE
821225
820228
821201
821201
821201
i
.
.
.
APPENDIX C
116
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABIE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
94
31
1 16
116
116
79
0
0
0
MEAN
70.8597
50.4974
43.2061
26 .8322
16.3740
0.6275
.
.
.
1 /AU /
STD
27.0568
19. 1904
21 .4916
14.7533
10.6490
0.2544
.
.
.
MAnt = wA5Mxn(j run <. ii aiKttr;
MIN MAX STARTED
27.6800
24.3300
1 1 .9300
4.9700
2.0900
0.1919
.
.
.
0 .
CTTTT rtQrtO^nO1Q*rt*' ir n M rป T.T 11 o Y_I T IT / n
N MEAN
47 65.9506
39
19
19
19
10
0
0
0
0
N
0
0
78
78
78
0
0
0
0
0
52.4046
33.8428
20.4137
13.4286
0.5108
.
.
SITE= 1043600
MEAN
.
35.6841
13.7337
21 . 9496
.
.
,
.
.
rt u / nn
STD
28.6001
22.2475
18.0001
1 1 .7577
15. 1914
0. 1008
.
.
.
35A07
STD
13. 6176
6.9098
10.3012
.
.
.
.
.
nc.-wMonjunu.i
MIN
22.390
21 . 100
6.403
3.850
2.553
0.286
.
,
NAME=TAMPA
MIN
.
12.16
4. 64
5.34
r
.
f
.
186.900
88.430
121 . 100
86.600
60.200
1 .594
.
.
.
(/** TV T> D T O
(j A KK. JLo
MAX
155.000
120. 900
79.470
49. 100
73.260
0.677
.
.
.
(DAVIS ISL
MAX
.
83.52
47.63
66. 16
f
m
t
.
.
790912
800602
790906
790906
790906
.
.
.
.
STARTED
800807
800801
810820
810820
810820
.
.
f
t
ซ ir
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FIKE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
N
105
42
102
102
102
88
0
0
0
0
N
61
25
54
54
54
50
0
0
0
0
N
0
0
75
75
75
0
0
0
0
0
a j. i r. = i iviuuu
MEAN
58. 3878
50.9874
35.7465
22. 1232
13.6228
0.5931
.
.
.
SITE=1 102000
MEAN
76.8887
65.6760
40.4713
23.4106
17.0606
0.4989
.
.
.
ITE=1 1450001
MEAN
.
41 . 1 187
17.8127
23.3066
.
.
.
.
f
U 1 AU / MAH
STD
20.4002
16.5209
14.7480
9.5788
8.4371
0.0895
.
f
m
r. = A i L A ซ i : A
MIN
21 . 1300
25.9900
11 .6500
6.4600
1 .9700
0.4168
.
B
f
39A07 NAME=ATLANTA
STD
31 . 1948
23.5914
20.2231
10.8555
13. 1732
0 . 1077
,
.
.
7A07 NAME
STD
.
19.2027
9.2414
14. 3478
.
.
.
.
f
MIN
29.5000
31 .2100
10.8900
9.2500
1 . 3900
0.2954
,
.
=SAVANNAH
MIN
.
9. 169
6.114
1 . 400
.
.
.
,
f
\ B V i it L. K i T
MAX
121 .000
92.840
77. 140
58.360
62.780
0.946
.
.
t
(MARIETTA
MAX
165.800
120. 900
94.310
60.510
59.440
0.755
,
.
.
(SCOTT MID
MAX
.
.
90.95
55.51
64.20
,
.
.
.
,
nm )
STARTED
800726
800720
800726
800726
800726
.
.
f
.
TJ T t t T\ N
a Lv u )
STARTED
800726
800801
800726
800726
800726
,
,
.
.
c r* u \
oUn ;
STARTED
810820
810820
810820
.
.
.
.
.
END_DATE
821219
810826
821231
821231
821231
f
.
END_DATi;
820312
810802
820312
820312
820312
.
.
.
r
END_DATE
821125
821 125
821125
,
.
.
118
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATIO 10
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
N
75
109
156
156
156
69
0
0
0
0
N
104
14
92
92
92
77
5
5
5
5XTi = 1 i
MEAN
34. 0871
22.5296
16.0729
5.5579
10.5154
0.4775
.
.
.
U 6 1 UUUHAU /
STD
8.59821
5.99244
6.62291
4.82660
4.89363
0. 17599
.
.
,
MIN
16.2700
5.4510
6.7400
2.0910
1 . 3200
0.2642
.
.
.
SITE=130220003A07 NAME=BOISE (
MEAN
90.3296
67.0679
37.9085
18.0052
19.9043
0.4178
52.4640
41.1160
1 1 . 3460
4 1.9117
OX1&-I4I44UU
N MEAN
28 71 . 1064
42
40
40
40
12
0
0
0
0
56 .0086
39. 1557
19.9560
19 . 1982
0 .4424
.
.
,
,
STD
49.2999
35.9070
21 .9680
15.2809
13.7253
0. 1258
23.0055
19. 3883
4.7330
2.9593
111 11 A *7 XfTIMIT
4 AU / jiAnt.
STD
26. 1455
33. 1 192
20 .6144
12. 1371
14.9754
0 . 1059
f
.
.
MIN
12.2200
24.4900
8.7620
1 .7600
1 .0600
0. 1942
15.8400
8.8500
7. 0000
0. 3800
r* u T r* R r* r\
-onXUAuU
MIN
32.700
24. 160
1 1 .560
4.650
4.440
0 .272
.
B
s
,
mil uj.li in
MAX
70.1100
50. 1 100
56.4400
55. 1200
37.0500
1 .5168
.
.
*
:FIRE STATI
MAX
294.500
129.500
1 13.000
75.700
71 .600
0.80.3
77.600
58.950
18.650
x ;
STARTED
790930
790930
790930
790930
790930
.
.
.
.
f\\r Jt ฃ ^
UN * O ) ~
STARTED
800825
8101 16
800825
800825
800825
.
821201
821201
821201
END_DATE
810522
81 1224
821003
821008
821008
.
.
.
.
END_DATE
821231
810416
821 125
821 125
821 125
,
821231
821231
821231
6.350
(f H O D ^ r\ T5 M T 'f f\ T5 V ^
r AKH DORnirORl > -
MAX STARTED
149.600 791030
224.700
90 . 360
67.760
60.950
0. 604
.
.
.
.
810215
810209
8 10209
810209
.
END_DR'
82082
8 1 11 C
82062
82062
82062
APPENDIX C
119
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
-j
N
34
29
58
58
58
22
0
0
0
0
N
55
1
32
32
32
22
0
0
0
0
N
87
32
59
59
59
43
0
0
0
0
j. X t, = |H \ 66\i\.
MEAN
104. 139
90.746
54.558
25.772
28.784
0.596
.
.
.
<3TTT 1 ti ^ Q ฃ
^ J. 1 ฃ* ~ 1 4 ฃ 3 C
MEAN
53.0584
35.7700
28.8593
27.9905
0.8695
0.4943
.
.
.
IZ2 AU / It
STD
38.2550
52.5663
24.6199
12.7936
16.8194
0. 1690
t
t
m
A n 1 n n fi "7
) U U I U A U /
STD
23.5680
.
16.6517
16.4775
0.551 1
0.0960
.
.
.
MIN
40.080
29.980
14.270
6.230
3.330
0.356
.
.
.
VTIVMf r*UTr*T
fiArlr. LปHiU*
MIN
21 .4800
35.7700
7.9600
7.3340
0.0170
0.3302
.
.
.
> I MA5n-LN;
STARTED
810203
810218
810203
810203
810203
.
i
f
n \i ^ _ ^
UN J ~ ~
STARTED
810721
81 1 130
810721
810721
810721
ป
.
.
.
END_DAt
8206K
81091:
82121'!
82121<
82121<
END_DATE
821231
811 130
821207
821207
821207
,
.
.
MEAN
61 .8728
43.6691
28. 1989
17. 1851
1 1 .0138
0.5177
.
.
.
,
E.UUU I H
-------
ENVIRONMENTAL PROTECTION AGENCY
INHAIABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SiTE= 15 ISiJ
N MEAN
31 1
21
34
34
34
29
0
0
0
0
N
69
40
41
41
41
34
0
0
0
0
N
54
41
0
0
0
0
0
0
0
0
22.716
84. 100
60.376
27.519
32.862
0.540
.
,
.
=15204002
MEAN
65.8303
52.0592
42.7248
23.0925
19.6323
0.6045
1ฃ?1AflfiO
i o ฃป i o u y u
MEAN
75.2919
63.0337
.
.
f
,
t
.
.
UU 1 OAU / N
STD
70.0487
39.9038
28.7440
1 1 .4360
23.5754
0 .0951
.
.
1A07 NAME
STD
27.6469
16.6862
24.4804
14.6218
13. 3687
0 . 1873
.
.
.
^ 71 n *7 vr 11 MT
& A \} 1 n Aflr*
STD
21 . 3769
18.3377
.
.
.
.
.
MIN
39.0500
47.4500
18.9200
9.9000
2.0800
0.4084
.
.
.
I t tULKAi. a
MAX
371 .00
223.60
152.80
51 .30
101 .50
0.71
.
.
=INDIANAPOLIS(MICHI
MIN
29.4400
25.4400
1 .5350
1 .0520
0 .4840
0.0219
.
.
= vJEFFERSO
MIN
33.98
25.77
.
.
.
f
<
i
.
.
MAX
163.500
94.800
99.720
60.850
63.610
1 .315
.
MAX
119.70
99 .45
.
.
B
.
m
f
.
.
.LUljJ
STARTED
810504
810504
810522
810522
810522
.
.
.
-
r* n M c? T ^ _
u Alt o 1 J
STARTED
801024
801018
82041 1
82041 1
82041 1
.
.
STARTED
801 129
801 129
t
.
.
.
.
.
END_DAT
820 101:
81112^
820105
82010E
82010E
.
.
END_DATE
821225
81 1 130
821225
821225
821225
.
f
END_DAT'
820306
81 1206
APPENDIX C
121
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABIE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
aj.it= i oฃ3uuu v
N MEAN
91 71
57 54
95 40
95 14
95 25
74 0
0
0
0
0
oX it,
N
89
40
102
102
102
76
0
0
0
0
N
128
0
0
0
0
0
0
0
0
0
.8529
.0282
.0168
. 1798
.8375
.5633
.
.
.
1 ฃ *> C A rt A A
1 D L 3U U U U
MEAN
47.081 1
38.3941
29.8501
13.6821
16. 1680
0.6498
.
.
.
-
17180001
MEAN
95.5305
,
.
.
.
t
.
.
,
.
3AU / ttAnฃ. = nAK;>ttAii
STD MIN
27.7463 26.2700
21 .0254 12.4500
18. 4777 0.8839
8.1196 0. 1239
13.8214 0.7600
0. 1721 0 .2899
r f
f f
t f
lj T U M ft 1 U X X I
MAX
150. 10
92.85
89.06
42.08
66.46
1 .75
m
f
.
ttAiiij;
STARTED
800813
800813
800924
800924
800924
.
.
.
END_DA1
82101H
81 1 1 IS
82101^
82101^
8210T)
|i ป rt ^7 \T Tl M f - M HQ^UHT T *1* m T\F ^TTC?LIfO OfLJ^
4AO / NAME-MARSHALLTOWN CFISHER SCH )
STD MIN MAX STARTED
19.2461 8.2080
16.4156 8.4050
16.1255 7.1450
7.6301 0.4040
12.8983 3.6500
0.1941 0.2259
. .
. .
.
1A07 NAME=KANSAS
STD MIN
34.9183 34.71
. .
.
.
,
f
% ^
. ,
. ,
. ,
123.700
82. 310
80.470
37.770
62.070
1 .363
,
.
.
CITY KS (FA
MAX
225.4
,
.
.
.
.
.
.
.
.
800825
8009 18
800819
800819
800819
.
B
.
T D V H V ^
J.Kr AX I
STARTED
800203
.
.
f
f
END_DATE
821 107
811118
821231
821231
821231
.
f
.
END_DATT
820417
.
APPENDIX C
122
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATI015=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
5J.1 ฃ.= 1 / 33DUUU / AU / 71 Ant- J. Ur r.rป A
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE 15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
120
67
71
71
71
54
0
0
0
MEAN
70.7816
56.4293
29.7087
1 1 .5973
18.1118
0. 4909
.
,
0
N MEAN
0
0
47
47
47
0
0
0
0
.
40.3438
13.5883
26.7549
.
.
.
.
0
N MEAN
22 106.255
9
1 1
1 1
1 1
6
0
0
0
0
53.814
77 .235
37.770
39.465
0.557
.
.
,
.
STD
28.0506
21 .7479
13.3024
5.6631
1 1 .0854
0. 1 102
.
.
.
MIN
22.9000
18.6800
12.2800
3. 1 100
3.4700
0.2694
.
,
.
l^mrt*7 U n M C* TIT^UTTH
IZAU/ nAnt.-WJ.unJ.TA
STD HIM
.
.
22.5294
6.2412
19.5395
.
.
.
.
,
10.13
3. 13
5.78
.
f
,
s
%O1IA'7 UKMC* HCUTHVfn
}{,Pi
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATIO 10
N
74
52
35
35
35
22
0
0
0
0
N
59
13
52
52
52
18
0
0
0
0
MEAN
83.6945
58.9271
42.6160
24.2134
18.4029
0.5545
.
.
.
S I T E * Z I 0 I 2000
MEAN
65.8546
63.2823
38.8227
22.7354
16.0867
0.5483
.
.
.
STD
29. 9507
19.8841
16.6173
12.0140
8.0913
0.0793
.
.
.
In ft T vf n Mf
A U / N Arlf.
STD
27. 0200
16.4637
17.8519
9. 9404
1 1 .3720
0.0820
.
.
.
SITE=210120008A07 NAME
N MEAN
35 70.3454
19 82.4195
20 32.8235
20 18. 9720
20 13.8520
10 0.5396
0
0
0
0
STD
35.7739
27.9840
18.7443
10.8032
10.5653
0.0835
.
.
.
f
MIN
36.0000
27.7300
1 1 .7400
6.4000
5.3400
0.4133
,
.
.
~ 15 H T T T M n O T?
-rSA.LrJ.nUKt.
MIN
22.7500
38.6600
4.7140
0.7100
2.4950
0.3822
,
.
.
=BALTIMORE
MIN
24.7300
43. 0800
12. 0900
6. 1300
4.2000
0.4152
,
.
f
MAX
234.50
136.50
83.56
53.59
41 .82
0.70
.
m
f
(fTOf T^rTlf
FIRE DEPT
MAX
141 .90
91 .99
83.70
49.24
47.29
0.68
.
.
.
(SE POLICE
STARTED
801229
801 1 17
82041 1
82041 1
82041 1
.
.
f
f
IT ^ ^
H2 ;
STARTED
800819
800819
810820
810820
810820
fc
r
.
.
-
C T Tl ^ ^.
b I A 1
MAX STARTED
163.300 80
145.400 81
85.660 81
50.980 81
50.710 81
0.674
9
f
.
f
1223
0329
0820
0820
0820
.
,
f
,
f
END_DAT
821231
811112
82123 1
82123 !
821231
.
END_DA'_
81 12 1C
81081'
82123'
82 123',
82123-
END_DATE
811218
810814
811218
8 1 12 IS
811218
.
t
APPENDIX C
124
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICUIATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SITE=ZIUlZUUUyAU/
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATIO 10
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
78
40
105
105
105
64
0
0
0
0
N
12
14
1
1
1
1
0
0
0
0
MEAN
55.8869
52.9522
34.5223
21 .4899
13.0328
0.6486
.
.
.
CTTV ^1 I^Of
oJ. !ฃ.-/. I lool
MEAN
53. 3075
39.2571
29. 1600
1 1 .2700
17.8900
0.4810
.
.
.
STD
21 .
22.
18.
12.
8.
0.
.
.
.
1 C\ A *> 11
) U U i, A
STD
20.
15.
.
.
.
.
.
.
.
NAnt = HAiiijLnuj
MIN
3490 20.4900
7028 16.7800
0910 8.0630
4928 5.0100
8995 0.4900
1994 0.3845
.
.
,
A *7 VT 71 M r Ortf*t/*T7^
U/ It Aril. RUCK V.
MIN
3587 30.690
6431 22.450
29 . 160
11 .270
17.890
0. 481
.
,
r
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
0 -L JL ฃ U \ lOOWWV/rtW/
N MEAN STD
46
0
57
57
57
38
0
0
0
0
51 .7057
.
29.7561
19 .6894
10 .0678
0.5910
.
.
.
16 .
.
1 1 .
9 .
5.
0.
.
t
,
MIN
4390 23.0400
.
2594 7.3720
1048 6.6440
8058 0.2500
1509 0.2791
.
.
.
.
K.E. kiW f U L J. U t & 1 A J
MAX
129.100
1 19 .900
91 .580
60. 920
54.820
1.512
.
.
.
(f* T 1* V
CITY
MAX
100. 300
78.670
29 . 160
1 1 .270
17.890
0.481
s
.
STARTED
790831
800819
790906
790906
790906
.
.
T t ซ T T1 \
HALL J
STARTED
801 105
801012
810820
810820
810820
.
.
t
.
END_DA-
821231
810814
821213
821213
821213
.
.
.
.
END_DA:
81 082C
810422
81082C
8 1 0 8 2 f.
810821
(M HDVTTRTf C? ^* XJ ^
nAKiVALi. bLMJ
MAX STARTED
105.600
55.810
42. 600
29 .700
1.081
.
.
.
811001
81090 1
810901
810901
END_DATE
821225
821225
821225
82 1225
APPENDIX C
125
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FIKE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
1 17
79
125
125
125
102
0
0
0
0
N
81
15
89
89
89
69
0
0
0
0
N
0
3
59
59
59
0
0
0
0
0
:>j..i& = ฃฃi>ฃ
MEAN
60.2476
46. 1576
33.4932
18.3777
15. 1 155
0.5500
.
.
.
ITE=22024001
MEAN
54.8154
37.8440
32.6363
17.5507
15.0860
0.5834
fc
.
.
SITE=2221600
MEAN
49.8867
29 .6002
17 .7317
1 1 .8681
.
.
.
,
.
4UU 1 i AU /
STD
21 .2297
18.3089
17.4185
9.9266
1 1 .2815
0. 1510
.
.
.
3A07 NAME
STD
16.3887
1 1 .2068
14.0355
9.6153
8.6546
0. 1946
ป
.
,
nAnฃ. = BUi
MIN
22.8800
9.7040
8.8530
4. 1 160
2.4620
0.2513
.
.
.
=BOSTON
MIN
16.7200
18. 1300
10.8600
4. 3700
0 .9400
0.3114
.
.
.
iiun ir-LKr.
MAX
124.700
105.400
140.600
54.280
105.900
1 . 128
.
.
,
(E BOSTON
MAX
96.4400
63.6400
80.7800
48.6300
64. 3700
1 .4616
.
.
.
11A07 NAME=SPRINGFIELD(HOWl
STD
25. 1775
12.2999
9. 1993
5.9679
.
.
.
,
.
MIN
25.84
10.99
5.51
3.48
.
.
.
.
.
MAX
76.06
68.62
42.56
30.02
.
.
.
.
.
nyjj
STARTED
791205
79121 1
791205
791205
791205
.
.
.
,
cor* r* T D ^
bUC CTR > ~~
STARTED
791211
810621
791211
79121 1
79121 1
.
.
.
.
\K.U aT J
STARTED
810703
810627
810627
810627
.
.
.
END_DATE
821207
811001
821026
821026
821026
.
.
t
t
END_DATE
811118
81 1007
81 1230
81 1230
81 1230
.
.
END_DATE
810907
820902
820902
820902
.
.
.
.
.
126
APPENDIX C
-------
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
0
2
7
7
7
0
0
0
0
0
29
23
16
7
.
.5700
.4071
. 1900
.2186
,
.
r
t
f
6
10
9
2
.
.9579
.8486
. 1845
.5664
.
.
.
.
.
24
1 1
7
4
.
.65
.56
.00
.49
.
,
m
m
f
.
34.
39.
29.
10.
.
.
t
f
.
49
02
21
09
8
8
8
8
.
10709
10627
10627
10627
.
f
.
.
.
8
8
8
8
f
10721
1 1025
1 1025
1 1025
.
.
.
.
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI0.15
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
0
2
7
7
7
0
0
0
0
0
N
0
14
60
60
60
0
0
0
0
0
N
0
0
43
43
43
0
0
0
0
0
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATI015 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SITE=222160011A57 NAME=SPRINGFIELD COLOCATED -
MEAN
STD
MIN
MAX
STARTED
SITE=222640016A07 NAME = WORCESTER (YMCA BLDG)
MEAN STD MIN MAX STARTED
SITE=222640016A57 NAME=WORCESTER(YMCA COD
MEAN STD MIN MAX STARTED
END_DATE
END DATE
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI0.15
DICHOT10
FINE10
COARSE10
RATI010
0
14 44.8179 10.7004
60 32.7175 14.3412
60 16.5327 7.9306
60 16. 1841 10. 4727
0
0
0
0
0
22.110 59.37 810609
7.542 78.01 810609
5.060 35.23 810609
1 .960 51 .36 810609
ป
.
810919
820815
820815
820815
.
.
33.3748
15.8894
17.4845
16.2171
7.3218
13.3109
8.738
4.950
2.543
78.71
35.83
64. 16
81 1031
811031
811031
END DATE
820815
8208 15
820815
127
APPENDIX C
-------
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATIO 15
DICHOT10
FINE10
COAP.SE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
54
30
0
0
0
0
0
0
0
0
N
44
43
0
0
0
0
0
0
0
0
N
64
47
0
0
0
0
0
0
0
0
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SITE=231180015A07 NAME=DETROIT (SOUTHWEST HS) -
MEAN
95.9763
76.7267
STD
41 .7213
37.4312
MIN
26.41
19.63
MAX
219.4
171.9
STARTED
800825
800825
END_DATE
811130
810727
SITE=231 180020A07 NAME = DETROIT (APC H2 BLDG) ---
MEAN STD MIN MAX STARTED
END DATE
TSP
SSI
DICHOT15
FINE15
COARSE15
RATIO 15
DICHOT10
FINE10
COAP.SE10
RATI010
44 80.4300 25.1442 40.96 136.8 800813
43 58.0505 22.4574 18.55 101.2 800912
0 . .
0 . . . .
0 . . . .
0 . . . .
0 . . . .
0 . . . .
0 . . .
0 . . . .
81 1224
811118
.
.
.
.
SITE=241040025A07 NAME=DULUTH (ELLIOT MEATS)
MEAN STD MIN MAX STARTED
66. 6805
46.7879
36.0385
24.4933
18.80
15.76
182. 4
110.5
800930
800930
END_DATE
81 1230
811130
128
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATI015 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATIO 15
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
25
24
0
0
0
0
0
0
0
0
N
84
0
128
128
128
79
0
0
0
0
N
73
77
144
144
144
66
0
0
0
0
:> a. 1 1 = ^ 4 IDI
MEAN
56.9584
39.9279
.
.
.
,
.
.
.
SITE=24226
MEAN
49. 1860
.
27.9039
14.4630
13.4408
0.6246
,
.
MEAN
73.0471
50.8023
36 . 0523
16.5850
19.4670
0.5889
.
.
.
.
UUU/AU/ nAiir.-J.ni r A j
STD HIM
26.5519 11.17
16. 1445 14.68
. .
. .
. ,
. .
, .
4 .
. .
LiliA V 1-
MAX
133
75
0049A07 NAME=MINNEAPOLIS
STD MIN
22.5144 15.6500
f B
12.7117 7.6220
8.3889 3.2850
8.2666 1.6100
0.2038 0.3438
. .
. .
. .
ft. ft. C 1 R ft. *7 WRMr MTUWPBT
U U 3 I AU / rlAnfc-n.JLnrlr.AI
STD MIN
35.0693 24.1600
19.3431 15.1500
17.6692 10.3700
13.2637 3.4300
1 1 .9624 0.9000
0.2425 0.3098
. .
. .
. ,
. .
MAX
124.
,
86.
60.
45.
1 .
.
.
,
3 rt T T C
3OLIS
MAX
220 .
128.
143.
142.
78.
1 .
.
f
m
t
u^iuri oijuu >
STARTED
.50 800924
.08 800924
.
. .
. ,
.
. %
. f
(^T*>"^4tป flC^ \
KฃuXnA HOJ -
STARTED
600 790924
f
960 790924
920 790924
730 790924
348
.
.
.
STARTED
400 791105
700 800515
900 791105
900 791105
300 791105
548
.
.
.
.
END_DAT
81 1007
81 1007
.
.
.
,
.
END_DATE
810305
.
820105
820105
820105
,
B
.
END_DATE
810323
81 1 130
82 120 1
82120 1
821201
.
.
.
.
.
129
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO 15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
a j. ij% = ฃH.s juu w v JAW / rt
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N MEAN STD
111 69.2670 24
56 52.5609 22
32 24.0316 11
32 14.0759 7
32 9.9560 6
31 0.3203 0
0
0
0
0
oJ_i.t,-ฃ3lฃoUUUoAU/
N MEAN
0
0
70 36.8231 16
70 18.1339 9
70 18.6897 12
0
0
0
0
0
N MEAN STD
74 66.0005 23.
29 43.0076 12.
75 35.8226 19.
75 17 . 9849 10 .
75 17.8381 1 1 .
43 0.6428 0.
0
0
0
0
.3544
.3581
.6926
.6750
.2103
. 1 148
.
.
.
-
NAME
STD
.
. 1977
.0510
.5392
.
t
.
.
1A07
581 1
1063
4712
9329
61 18
1694
Ant-ai rAuii <.rj.K.r. &IAJ
MIN
24. 1000
14.5300
7.6810
5.3900
1 .6820
0. 1725
.
f
f
=JACKSON(
MIN
.
15. 15
6.79
3.57
.
t
,
,
-
MAX
160.70
139.70
60.61
35.62
30.48
0. 68
.
.
.
SUN ฃ SAND
MAX
B
82.00
53.70
67.54
,
f
,
f
NAME=ST LOUIS (AFTOI
MIN
27.090
20 .360
3.529
0.739
2 . 668
0.295
.
,
t
.
MAX
137.600
68.430
85.400
48. 440
46.530
1 .084
.
.
r
.
STARTED
800930
800930
820330
820330
820330
.
,
,
,
lu* rx m T" T ^
MOTELJ
STARTED
f
810814
810814
810814
.
m
.
.
ir \
ft i ~
STARTED
800128
800726
800203
800203
800203
t
t
f
.
.
END_DATE
821225
811112
821201
821201
821201
.
.
,
END_DATE
821213
821213
821213
.
.
END_DA'
81111:
81102:
82123
82123
82123
130
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATI015 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COAP.SE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
1
1
1
1
N
53
52
19
19
19
0
1
1
1
0
N
0
0
13
13
13
0
0
0
0
0
N MEAN
03 85.4416
62 64.6663
28 42.8073
28 17.0630
28 25.7439
91 0.5323
0
0
0
0
- SITE=264280
MEAN
89.5632
68.51 17
48. 6321
22.7295
25.9032
.
29.0600
17. 1700
1 1 .8900
MEAN
.
26.5546
8. 9715
17.5823
.
,
.
.
.
&AV I itA
STD
28.4298
20. 3429
18.2346
9. 1738
13.6113
0.0950
.
.
.
007A07
STD
32.5263
2 1 .6745
22. 6593
9 .4058
18. 1033
.
.
.
.
STD
,
19.4535
6. 1682
14. 1554
.
,
.
.
nr. = N Aซaaป
MIN
29.830
28. 380
10.410
4.710
3.090
0. 349
.
,
.
u j. i i nu v
MAX
161 .000
121 .700
92.030
56.040
61 .580
0.937
.
,
NAME=ST LOUIS ( S BR
MIN
32.80
17.53
17.23
7.62
8.27
f
29.06
17. 17
1 1 .89
VfRMP BTITTT
rlAnt-BUTTE
MIN
10.13
3.55
3.82
.
f
.
.
,
MAX
199.20
124.70
106. 10
41 . 97
76.70
m
29.06
17 . 17
11.89
(^ D r v T v
GREELY
MAX
,
80.71
25.86
54.85
r
t
m
f
.
r J.KI. a i A >
STARTED
800209
800209
800209
800209
800209
.
.
.
^\ซป\TYป*J\
UAUWAl ) -
STARTED
800427
800427
820417
820417
820417
.
821207
821207
82 1207
r^s^ttA/^T ^
SCHOOL.)
STARTED
820222
820222
820222
.
.
.
END_DATE
820423
810410
821231
821231
821231
.
.
,
.
END_DAT
81 212
31 106
82 125
82 125
82 125
821207
821 207
82 1207
END_DATE
.
820530
820530
820530
.
l
131
APPENDIX C
-------
I
ENVIRONMENTAL PROTECTION AGENC*
INHALABLE PARTICIPATE NETWORK
:NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE 10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE1S
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
i-i
N
0
0
2
2
2
0
0
0
0
0
N
125
73
30
30
30
27
2
2
2
2
N
123
66
19
19
19
18
5
5
5
5
.!&-ฃ/ 1 1 U U VJ
MEAN
.
.
29.97
13.83
16. 14
.
.
.
.
CTTV 9Q 1 fl
oil ฃ.- ฃ S 1C
MEAN
66.5054
52.3593
43.9803
15.2760
28.7057
0.6675
36.6300
1 1 .7650
24.8700
0.8319
CTTP *} Q ft t
Jilt- ฃ 7 U l
MEAN
85.3645
65.8103
34.091 1
13. 1 184
20.9721
0.4962
49.9640
29.5280
20.4340
0.4831
< f. V AU / Jtf
STD
.
.
16.8150
8.4004
8.4146
.
.
.
.
>aAA*A1|A'7
loUUloAU /
STD
21 .6748
17.7535
17.0358
8.0878
12.6672
0. 1 107
0.8061
0.8132
0.0141
0.1161
i ft o o rt 1 m n *7
40UUU I A U /
STD
47.6322
47.8706
15.0020
7.6266
9. 1474
0. 1173
20.761 1
15. 1312
8.0315
0. 1179
MIN
.
,
18.08
7.89
10. 19
.
.
.
.
V H M V rt M H U H
NAnt-UnAHA
MIN
27.6800
16.4000
21 .6700
7.2100
9.5400
0.5021
36.0600
1 1 . 1900
24.8600
0.7498
WHMt* DFWft
riArlE* KtปHU
MIN
23.2300
14.8100
12.8600
3.3700
9.0600
0. 1656
27.9700
1 1 .4000
14.4700
0.3618
I KVOl.lt*
MAX
.
.
41 .86
19.77
22.09
.
.
.
.
(f\ 9 1* O C
U 5TRE
MAX
131 .500
104.300
91 .730
45.570
72.680
0 . 942
37.200
12.340
24.880
0.914
(V T O M H V
K X Rri Art
MAX
312.000
262.700
72.420
31 .590
40.830
0.727
75.080
42.610
33.810
0.667
STARTED
.
820412
820412
820412
.
.
.
.
STARTED
800726
800726
820529
820529
820529
..
821207
821207
821207
-------
EMVIRONMEMTA1 PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 1 0 = DICHOT 1 0/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE 10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE 15
P.ATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
113
0
105
105
105
78
0
0
0
0
N
123
51
72
72
72
63
0
0
0
0
N
122
62
1 16
1 16
1 16
1 1 1
0
0
0
0
51TE=Z^
MEAN
53.7317
.
28. 9727
8.3378
20.6354
0.5590
.
.
.
MEAN
67.3548
54.7733
36.0277
20.6529
15.3751
0.5338
.
.
MEAN
44. 2846
38.2929
26.9250
16 . 4775
10.4475
0.5932
.
.
.
,
JU30UUU 1 AU
STD
31 .701 1
.
20.5586
6.4339
19.6804
0.2087
.
.
.
STD
24.2149
21.9726
16.3349
10.3978
9.8758
0. 1299
.
.
.
STD
17.5462
15.6008
14. 0050
10.9794
6.6946
0. 1976
.
.
.
.
/ rtAriฃ. = w
MIN
12.9100
.
5.0650
2.4700
0.2100
0. 1638
,
.
.
H ft "7 MUMP
A v / ft Anr.
MIN
24.4800
22.5500
8.6100
3.7650
4.4100
0.3016
.
.
.
"7 Vf S M F T
/ ft Ant, L
MIN
1 1 .2100
1 1 .4500
5.7730
3.0320
2.4250
0.3352
f
t
f
.
xjtNtnuuuA
MAX
267. 30
.
158.80
52.87
137.40
1.19
.
.
.
MAX
152.200
105.600
87.370
61 .250
70. 050
1 . 368
.
.
*
TWTWfCTrtU
XV Iftljb TUN
MAX
100.90
88.01
71.81
58.53
43.89
1 .67
.
.
.
.
STARTED
790930
.
790930
790930
790930
.
STARTED
800918
800918
810826
810826
810826
.
.
.
STARTED
80080 1
80121 1
80080 1
80080 1
80080 1
.
.
.
END_DATE
821002
820920
820920
820920
,
,
.
END_DATE
821 101
810814
821213
821213
821213
.
.
.
.
END_DATE
821020
820 1 1 1
821020
821020
821020
.
.
133
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATI015=DICHOT15/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSS10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
ปXJ.ฃ*~JIซiJซ*VVV^AV/ f\l\i
N MEAN STD
96
43
58
58
58
54
0
0
0
0
N
95
36
96
96
96
78
0
0
0
0
N
1 10
48
102
102
102
92
0
0
0
0
74. 6031
55.3428
33.6091
19.8609
13.7481
0.4696
.
.
.
CTTP ^^Artfi
ฃ>XTL~ 36UU4
MEAN
88.4602
60.4831
36.6908
12.0147
24.6750
0 .4431
.
.
.
23.5042
20.6278
13.0065
10. 1495
5.4641
0.0592
.
.
.
IH rt "7
A U /
STD
42.0067
26.7067
21 .5507
9.5300
14.8705
0. 1244
.
.
.
SITE=320090001A07
MEAN
1 16 .274
75.378
73.806
14 .594
59 .212
0 .632
.
.
.
m
STD
45. 9839
27.2031
37.0823
9.0977
33.7353
0. 1998
.
.
.
.
RATI010=DICHOT
MP T TO ^ P V PTTV f H S V
riฃ,-wC,A^C*I UX 1 I I 0 A I
MIN MAX
38.2000
23.5100
15.2400
7.4500
6.0100
0.3216
.
.
.
\f R M f 11 T T3 TI O 1
nAnt-ALDUSJl
MIN
34.9400
22.3900
9.6800
3.5100
5.3540
0.2212
.
.
NAME=BAYARD
MIN
27 . 3200
14.9300
7.5800
5. 1000
1 .9850
0.2253
,
.
.
.
152.700
108.600
86.620
67.080
26 .810
0.613
.
.
.
_
MAX
228.200
1 15.600
124.400
51 . 300
83.000
1.211
.
.
.
-
(COBRE
MAX
251 .00
122.30
265.30
72.30
236.50
1 .53
.
.
.
f
10/HIVOL
STARTED
800924
800924
810820
810820
810820
.
.
.
VM f H > _
inCAJ
STARTED
80 1 123
801 123
810329
810329
810329
.
.
** f* \ 1 O rt T ^
iiUMUULJ -
STARTED
80121 1
801229
801217
801217
801217
.
.
.
t
END_DATE
821101
810814
821026
821026
821026
p
.
.
.
END_DATE
821008
810703
821225
821225
821225
.
.
END_DATE
821231
811130
821231
821231
821231
.
134
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATI015sDICHOT15/HIVOL . RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT-10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
N
75
24
115
1 15
1 15
65
0
0
0
0
N
1 16
70
164
164
164
97
37
37
37
33
N
0
0
7 ^
7 il
74
0
0
0
0
0
- 5iTE= i JUOOUUUiAU /
MEAN STD
85.2175
70.3829
66. 1270
39.8904
26.2372
0.7315
.
.
.
38. 3430
27.3887
30.5594
20.9262
15.7148
0.2309
.
.
.
- SITE=330660010A07
MEAN
85.2124
56.8447
44.4356
24.4691
19.9671
0.5182
34.9665
19.9614
15.0038
0 . 4748
MEAN
46.3204
21 .8078
24.5126
.
.
.
.
STD
35.8358
23. 1515
20.6879
1 1 .8448
13.8953
0.1615
17.6147
9. 3905
10. 9943
0. 1050
STD
23.2546
1 1 . 1357
15.6987
B
.
.
.
.
MIN
25. 1400
22.6400
17. 1500
6.3400
4.9900
0.3724
.
.
.
ALU ira ปฃOJ
MAX STARTED
160.400
136.600
143.700
104 . 100
73.000
1 .641
.
,
,
NAME=BUFFALO (PS t:
MIN
24.4200
15.8400
9.5200
2.7590
1 .2800
6.2090
10.2000
5.9600
2. 9900
0.2838
MUMP BITPfH
ft Ant. -Burr *
MIN
.
13.64
2.71
3.45
.
B
t
f
,
MAX
191 . 100
137.900
106.700
58. 140
69.100
1 .344
80.080
50.270
50 . 370
0 .786
[ T n f w 4 *) o
iLU t PS ป Z 8
MAX
.
129.80
55. 01
86. 40
.
.
.
f
790825
810528
790831
790831
790831
.
.
STARTED
790831
810603
790825
790825
790825
|
820318
820318
820318
/^ rt T A
STARTED
8 10522
810522
810522
.
END_DATE
810227
811019
820129
820129
820129
.
.
END_DATE
821231
821231
821231
821231
821231
821231
821231
821231
END_DA7
821231
82 1231
821231
.
.
135
APPENDIX C
-------
ENVIRONMENTAL PROTECTIOK AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATIO 10
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
ail
N
76
26
141
1 41
141
64
0
0
0
0
N
72
80
74
74
74
9
4
4
4
&= 531UU UU<
MEAN
37.9521
40.7573
41. 1334
20.4571
20.6773
1 . 1874
,
.
.
MEAN
1 19.347
76.367
44. 103
22.010
22.094
0.376
23.512
13.402
10. 107
0
N MEAN
0
25
0
0
0
0
3
3
3
0
85.6196
.
.
24. 1933
14.0667
10. 1267
.
U JAU / JtAH
STD
18.4760
17.9716
33. 1529
12.8742
24.9688
0.8963
.
t
.
In n *7 u n Mr*
AU / NAnr.
STD
53.3069
36.4593
38.7418
12.8690
30.0980
0-.3025
5.9624
3.4034
2.7858
1H C *7 W A M V
Ao / JiArlz,
STD
46. 1220
.
.
.
.
6.2674
3.3054
2.9892
.
fc = AJKjUliA
MIN
5.9390
1 1 .8100
1 .4640
0. 1750
0.2400
0.2081
B
%
,
(.J5J.VJ SJ.S
MAX
84.640
78.390
171 . 100
68.500
134.800
3.991
m
f
.
QTYPPUT rt ^ T 1 T T M T 1 H* U
-DUrrALOvWXLnUTn
MIN MAX
20.4900 300.400
24.5700
0.6921
0.5819
0. 1 102
0. 1490
16.2500
10.0800
6. 1800
1 I IT T MIITU
uix LH urn
MIN
42.20
.
17.05
10.26
6.79
.
204.800
198.600
59.940
149.600
1 .082
29.190
16.610
12.570
n r i M n C? *T* l\
r* uni* o r A
MAX
229.90
.
28.77
16.21
12.56
.
1I.K o 1 c i
STARTED
790825
810522
790825
790825
790825
t
f
.
n ft M n * m M ^
rUnP 3TAJ ~
STARTED
790918
800503
791030
791030
791030
.
821207
821207
821207
STARTED
810528
821207
821207
821207
.
END_DATE
810317
811031
821002
821002
821002
.
.
.
.
END_DATE
810522
81 1031
821201
821201
821201
.
821231
821231
821231
EHD_DAT'
81 1031
821231
82123'
821231
APPENDIX C
136
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
. COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COAP.SE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
62
28
72
72
72
58
0
0
0
0
N
121
20
0
0
0
0
0
0
0
0
N
66
4
53
53
53
48
0
0
0
0
51TE= 4 J40CUUU3AU / NAI
MEAN STD
62. 1744
60.3386
35. 1569
21 .8686
13.2885
0.5662
.
.
.
22.6360
19.3043
14.5516
9.6778
8.3106
0. 1228
.
.
.
it, = ni uj.ii
MIN
28. 6100
28.7000
14.4000
6.2500
3.4800
0.3626
.
.
CTTF 7TttฃArtrt* *mrt*7 VTHMP-.VIV /" T ฅ v
oXT*. Jj'rOOU
MEAN
75.8486
63.0730
.
.
.
,
.
MEAN
71 .2529
72.7050
34.9877
24.2140
10 . 7740
0.4617
f
m
,
vi i H v / r\ MI !ฃ - r\ i, v* j. A i
STD MIN
26.4596 19.78
23. 1741
.
.
.
.
,
.
t
rt *7 Q * rt "7 U 1
u / y AU / rt i
STD
22.5843
16 . 1029
15.4268
12.9493
5.9962
0.0791
f
f
f
,
34.96
f
.
.
.
.
.
t
\ M r w v ^* T *r* v
\nt. -rl I CiT I
niN
31 .5700
59.7700
10.9900
7. 3900
0 . 3700
0.2502
.
.
f
,
I Uf.Xri.KAli
MAX
135.000
99.660
82.860
49.320
55.890
1 .226
.
.
,
f fฐ D V V VI D
v (j tf.Lt.fi r
MAX
163.1
123.2
.
.
.
%
t
.
.
(T V1 1* O ^ U
INT SCH
MAX
144.700
96 . 220
88.760
71 . 000
25. 490
0. 626
.
.
STARTED END_DATF
810221 820517
810227 810820
810221 820517
810221 820517
81022 1 820517
.
. .
.
STARTED END_DATI
800614 821026
81022 1 810820
.
. t
.
M It C ^
WHO)
STARTED END_DATE
810802 821231
810802 810820
810802 821201
810802 821201
810802 821201
.
137
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHAIABLE PARTICULATE NETWORK
'NETWORK DATA SUMMARY
RATIO 1S = DICHOT15/HIVOL RATIO 1 0*~DICHOT 1 0/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE 10
RATI010
N
94
33
90
90
90
84
0
0
0
0
N
45
42
38
38
38
32
8
8
8
7
N
30
34
14
14
14
4
3
3
3
0
aj.ii = .
MEAN
60.2541
50.0379
37.0531
24. 1214
12.9314
0.6186
.
.
.
CT*PF-'3li1 1 A f
OX 1 I* - J 4 1 lot
MEAN
58.0046
44.4507
35.7276
23.8789
1 1 .8487
0.6405
29. 31 12
22.6725
6 . 6400
0.5766
MEAN
58.8025
43.6899
33.9387
24.4204
9.5176
0.4621
21.3133
17.0800
4.2333
f
S4 U / UU U 1
STD
19.7319
17.6812
15.7410
10.2306
9. 3894
0.2141
.
.
.
% ซ A ฃ. ft f\ -7
} U U u A U /
STD
21 .0882
18. 1227
16.6609
12.6023
5.4127
0. 1094
12.5306
9 . 1376
3.6569
0. 1235
f\ fL B C "7
U O A 3 /
STD
22.7175
19.7978
19.5986
14.2771
6.0570
0.2815
9.6350
7.8690
2.3170
t
VAU / rtAru:
MIN
25.70
20.75
12.59
9.25
0.26
0.29
.
.
t
xiBMr* nitot
n AH fc UURr
MIN
8.4480
18.6500
1 1 .0000
8.9800
1 .0600
0.4239
14.0900
10 . 4900
1 .5700
0 .4004
VT1MF HMDU HV<
nArlc. UUKnAr
MIN
8.9860
4. 1950
0.7715
0.0453
0.7262
0.0859
13.4200
9.6300
2. 1700
m
. = un AK.LU i a. r. -
MAX
108. 100
80.530
82.750
53.270
48.510
2.072
.
.
B
STARTED
810504
810504
810504
810504
810504
.
f
END_DAT
821231
811130
821231
821231
821231
.
.
(r* ปซ T* ^% ซ f T\ f* \
MAX STARTED
111.700 800503
100.200
83.730
66.370
22.480
0.861
52.900
39 .790
13.110
0.752
f /ซ ซ M r* n n T n f
1 ^, U A ric* U a l+Ufj
MAX
106.500
101 . 000
73.830
51 . 840
21 . 990
0.719
32.050
25. 310
6.740
f
800515
801 123
801 123
801 123
.
821002
821002
821002
STARTED
801117
801117
80 1 1 17
801117
801117
.
821201
821201
821201
.
END_DATE
821213
821213
821231
821231
821231
.
821231
821231
821231
'
END_DATE
811031
811031
821231
821231
821231
.
821231
821231
821231
.
138
APPENDIX C
-------
RATI015
ENVIRONMENTAL PROTECTION AGENCY
ZNHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
'DICHOT1S/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
N
102
98
92
92
92
87
0
0
0
0
N
0
0
55
55
ITE= a** i TOO 10
MEAN
40. 1913
35.0419
24.5704
17.6897
6.8814
0.6377
.
.
.
C? T T I" ป O (i 1 1 ฃ A 1
SITE- o 4 1 IbU 1
I1EAH
.
28. 1458
19.7273
55 , 8.4187
0
0
0
0
0
N
36
43
19
19
19
15
22
22
22
17
.
.
SITE=341 160
MEAN
37.2967
33.7460
26.9442
16. 3537
10.591 1
0.7343
20.7480
18.8131
1 .9340
0.5348
1 AO / MA
STD
16.8379
13.5610
13. 1187
12.3267
4.7622
0.2785
.
.
.
nr. = Kti IKJ.AJ
HIN
13.3400
16.4100
9.5100
4.6620
0.9200
0.2033
.
.
.
01 H C *7 UHMC*~D7C *T* tt T
1 Ao / ftAnt.-Kc.5 TRX
STD HIM
.
14.0850
1 1 .8008
4.6331
.
,
.
102A07
STD
13.5520
13.7957
1 1 .0334
6.3484
9. 1912
0.1415
9.3486
9.0080
2.0908
0. 1342
.
11 .82
6.94
2.08
.
.
.
1U.LC. ris lot
MAX
86.490
73.270
1 15.400
114.400
27.960
2.541
.
.
.
B L* f "DT*H TTWTT
F K t AV A U MX T
MAX
.
80.66
67.79
24.91
v
,
t
f
NAME=RES TRIANGLE PK (
MIN
16.4000
13.7300
1 1 .6000
7.6900
1 .6000
0.5158
8.4350
8.3280
0. 1000
0.2696
MAX
67. 1 100
69 .8200
60 . 5600
26. 3900
40.3900
1 .0760
39.3400
38.9800
7.6700
0.7099
STARTED
790726
790726
790726
790726
790726
.
.
.
CUL ; -
STARTED
.
81031 1
810311
81031 1
.
.
.
.
-
B T T > ^
STARTED
820105
820105
820105
820 105
820105
.
820517
820517
820517
.
END_DATE
811230
81 1230
811230
81 1230
81 1230
.
.
.
.
END_DATE
.
820628
820628
820623
f
.
.
.
END_DATE
820926
820926
820622
820622
820622
820926
820926
820926
f
139
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO 15ปDICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FIHE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE 10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SJ.1
N
94
107
185
185
185
90
0
0
0
0
N
86
85
159
159
159
71
0
0
0
0
N
1 19
26
108
108
108
86
0
0
0
0
C.= SOU UOUU 1
MEAN
67
53
46
25
20
0
.81 12
.6532
. 1354
.9864
. 1481
.7041
.
.
.
*ปAU /
STD
26.
19.
20.
12.
10.
0.
.
,
.
HAJI
4723
7364
5533
9775
9778
1483
ฃ.- AN
MIN
21 .
16.
8.
1 .
3.
0.
.
.
,
Kun v r
0700
2900
4310
2900
5520
3259
lUKi.1.
MAX
125
105
1 16
93
58
1
i nz.A.b
.000
.800
.800
.400
.820
.213
.
.
f
MEAN
57.5659
51
41
24
16
0
.4578
.0723
.9979
.0751
.7286
.
.
.
t. y H v
STD
23.
17.
17.
12.
9.
0.
.
.
.
/ n.Miic.-wxnifTปT a irn
bl T t.- 30 J JU
MEAN
1
30 .804
88. 678
70.083
31 .433
38.655
0.549
.
.
.
.
VI VI 1 OH U /
STD
57
38
42
25
25
0
.2081
.8729
.3196
.4631
.7186
. 1577
.
,
.
.
MIN
35
21
1
0
0
0
.820
.010
.209
.791
.418
. 170
,
.
.
.
*i
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
31
17
28
28
28
22
0
0
0
SITE = SO 1 JUUU
MEAN
55.4506
45.4535
38.4999
26.2486
12.2509
0.7344
.
.
.
0
N MEAN
98
39
62
62
62
53
0
0
0
0
N
72
54
0
0
0
0
0
0
0
0
82.5370
61.8344
44.3373
24. 1266
20.2092
0.5440
,
CTTTT* "3 C 1 ฃ1 ฃ ft ft A
.b .L 1 ฃป - O O 1HDUUU
MEAN
66. 1536
51 .7048
.
.
.
.
t
.
.
Z 1 AU / NA
STD
19.6017
20. 1005
18.3531
14.4835
6. 1332
0.2898
.
.
.
H ft *7 W R MTT
A 0 / rl Ant*
STD
24.6925
15.6819
18.8341
1 1 .7072
1 1 . 1407
0. 1022
.
.
.
IH ft *7 W n M
A U / ft An
STD
19.5274
17 . 1420
.
.
f
.
B
.
.
nC = ULฃVฃ,LA
MIN
28.510
10.830
7.938
5. 162
2.775
0.479
-
,
.
f*T VM V T HVfn
-CLC.Vc.LANi;
MIN
40.4100
35.5300
14.7600
6.8100
4.5400
0.3475
.
.
.
MIN
32.56
23.54
.
.
.
f
.
.
HU IKMUUC.
MAX
92.5200
84.4300
75.3100
61 .8900
26.2600
1 .6649
.
.
a ns;
STARTED
800203
810802
800203
800203
800203
.
.
END_DAT
820306
811106
820306
820306
820306
WAbHINuTON rK 1 "^
MAX STARTED
156.300
1 1 1 .900
86.610
59 .850
62.280
0.906
.
.
(
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10.
RATI010
SAMPLER
TSP
SSI
DICHOT15
FIKE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
RA
N
81
9
77
77
77
58
0
0
0
0
N
60
40
74
74
74
50
0
0
0
0
N
44
35
32
32
32
24
0
0
0
0
TI015=DICH01
SITE=36166(
MEAN
65.9064
61 .6489
36.2321
21 . 1960
15.0366
0.5510
.
.
.
M5/HIVOL
5014A07
STD
22.5836
21 .8224
15.5217
10.8670
8.5447
0. 1003
.
.
.
RATIO 10
MIN
23.5900
37.7600
12.0900
5.9200
3.7300
0.3468
.
.
,
CTTF ^ฃTflftflrtinnrt"7 v' ปซ vซ/Mrtiปซ
bXit-JDiUOUU 1 U A U /
MEAN . STD
73.6277
57.0032
40.8057
22.8718
17 . 9348
0.5830
CTT*Yป O ฃ li 1 til
5J.Tt.-oOH I HI
MEAN
48.9784
42.0848
33.6125
20 . 1650
13. 4457
0.6569
.
.
.
.
27.7747
22. 1772
19.0255
1 1 .8640
10.8161
0. 1731
.
.
f\ rt rt v K rt "7
0 0 U Z A U /
STD
20.8874
20.5559
15.7367
10 .2542
9.2103
0. 1584
.
.
.
t
MIN
25.9200
21 .8300
0.9628
0.1413
0.8215
0.3651
.
.
.
U H Kf C" ^ M T" T^ T \l H
HAnE-nEDIMA
MIN
12.5700
1 .8360
7.7810
5.8600
1.9210
0.2479
.
.
.
.
=DICHOT1C
(E MONUf
MAX
138.900
90.810
79.500
55.930
48.420
0.843
.
.
,
)/HIVOL
STARTED
801205
810227
810802
810802
810802
.
.
END_DATE
821002
810715
821231
821231
821231
.
.
f
f
(unfnTT*nT ^
HO5PITAI.J ~~
MAX STARTED
176.700
121 .900
124.400
75.540
75.300
1 .479
.
t
.
801018
801018
801024
801024
801024
.
.
END_DATE
820324
810721
820324
820324
820324
.
.
.
.
( t vvซซซ*wซM*ซr\
W LIBERTY 1
MAX STARTED
106 .500 800122
81 . 100
89 . 160
49. 990
39 . 170
0.973
.
,
.
f
800421
800421
80042 1
80042 1
.
.
.
f
END_DATE
820222
81 1 130
811001
811001
811001
.
.
.
.
142
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
130
78
39
39
39
38
0
0
0
0
C T T r
SITV
N
1
0
0
0
0
0
0
0
0
0
C T TP
O X I C.
N
79 1
99
52
52
52
21
29
29
29
6
MEAN
90.6561
62. 1697
49.3882
26. 1497
23.2379
0.5126
.
.
f
7 ฃ It O fi f\ f\
j O H o 4 U U
MEAN
44.52
,
.
.
.
.
.
o c ฃ ii ^ n A
3 o o H L U U
MEAN
10.538
80.962
55.980
33.926
22.057
0.567
41 . 178
25.568
15.610
0.305
STD
41 .7512
27.2833
21 .6839
13.3881
1 1 .9854
0.0793
.
.
.
ft C R C *7 W H M P
MIN
34.5200
27. 1400
17.5700
7.2000
8. 1500
0.3426
.
.
.
M T ^ n T ซ f
U 3 A 3 / ftAnc*-iij.isuijฃ.x
%
STD nix
44.52
,
,
.
.
.
.
.
.
1 ^ H O "7 W 8 MP
I L A u / n An L -
STD
50.3958 1
39.5762 1
34. 1606
20. 6970
16.5917
0.2382
22.4307 1
12.6105
1 1 .3356
0. 1726
_
.
.
.
.
.
.
.
MAX
230. 10
153.50
94.23
61 .33
61 .08
0.68
.
.
f
(f* R vi f* r
U Ariu L
MAX
44.52
^
.
.
.
.
.
STARTED
800912
800912
810820
810820
810820
.
.
f
STARTED
801117
f
f
.
END_DATE
821225
811212
821207
821207
821207
.
f
.
.
END_DATE
801117
.
.
.
.
f
CTPTTBlTlJt/TTTr' fIfHCUT\T/^'?ปrvvf>
bTc.Uoc.n V ILLt 1 W Ao n J.NCj TON ;
MIN MAX STARTED
8.5000 218. 000 79052 1
6.9400
8.0120
7.3120
0 .7000
0.0765
3. 4800
8.3700
2.8800
0.0824
210 . 500
148 . 000
90 . 800
88 . 600
0.905
90 .510
49.400
46 .760
0.520
790527
790831
790831
79083 1
8201 17
8201 17
8201 17
.
END_DA?E
821219
821219
821219
821219
821219
821219
821219
821219
.
143
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETUORK
NETWORK DATA SUMMARY
RATI015 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE 15
RATI015
DICHOT10
FINE10
COAP.SE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
0
0
31
31
31
0
0
0
0
0
N
129
65
1 14
1 14
1 14
109
6
6
6
6
N
65
30
8
3
8
6
0
0
0
0
- 3DOH4UU 1
MEAN
.
46.7352
29.4884
17.2474
.
.
.
.
MEAN
90. 3378
65.5122
46. 0467
22.9404
23. 1054
0.5007
45.7900
29 .8417
15. 9483
0.8735
IIA3/ AAHฃ.
STD
.
26.91 18
20.2320
9.2287
.
.
.
.
)flfi^Brt"7 Wfl
I U U i A U / NA
STD
38.4085
28. 1823
22.0133
12.2239
13.4187
0.0839
12.8580
8.0686
15.6629
0.5204
=372200035A07 NAME
MEAN
65.4011
52.0317
42.6912
17.9825
24.7087
0.6002
.
.
.
STD
22.01 15
21 .3776
13.4519
6.7223
9.6320
0. 1800
.
.
.
t
-a i C.UBC.N vj
MIN
.
15.26
8.60
4.63
,
.
.
.
MIN
24. 1300
25.5400
9.9980
6.0300
3.6000
0.2783
30.8000
22. 3400
1 .5600
0.4930
=OKLAHOMA
MIN
21 . 1200
17.9400
13. 3700
6 . 9300
6.4400
0.3783
.
.
.
,
L.L.LI.I w:>niปi A
MAX
.
145.20
1 1 1 .80
38.41
.
.
,
MAX
249 .200
164.200
126.000
79. 100
76.300
0.723
67.830
43. 440
45.470
1 .834
CITY (FIRE
MAX
132.700
101 .700
54.790
30 . 240
37. 150
0 .907
.
.
.
9
STARTED
820117
8201 17
8201 17
.
,
.
** T* ft ^
STARTED
801018
801024
801018
801018
801018
.
821201
821201
821201
-
C T* R > __
STARTED
810221
810221
810814
810814
810814
.
.
.
.
.
END_DAT
821219
8212 19
821219
END_DATE
821231
811212
821 125
821 125
821 125
r
82 1231
82 1231
821231
END_DATE
820604
811130
820222
820222
820222
.
.
.
.
144
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICMOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATIO 10
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
80
65
149
149
149
63
0
0
0
0
N
88
71
86
86
86
81
0
0
0
SITE=i*
MEAN
35
32
24
12
11
0
SITE
.3596
.6616
.0821
.4191
.6628
.9192
.
.
.
JU5UU
STD
25.
15.
16.
10.
1 1 .
0 .
.
.
,
1UHAI
9104
2920
7978
1635
2086
5131
=380560013A07
MEAN
49.
39.
30.
17.
13.
0.
,
.
.
6715
9749
6988
1653
5334
6169
0
N MEAN
89 75.3306
98
170
170
170
82
1
1
1
0
55
47
19
27
0
53
33
20
.9779
. 6848
.8023
.8826
.7505
.2600
.2400
.0200
.
STD
25.
21 .
19.
12.
1 1 .
0.
f
f
.
i c 71 A n
1 3 A U /
STD
42.
32.
37.
15.
28.
0.
.
.
.
.
6505
4478
6719
4902
7175
3035
VI 1
nl
6009
3338
4779
2206
9433
4007
;/ MAnE=bAi
MIN
8.01100
7.07200
2.95900
1 .68700
0.76300
0.38303
.
.
.
NAME=EUGENE
MIN
7. 178
1 1 .930
3.865
2.238
1 .484
0.374
B
t
.
IMP ns\ninT 11 \r T\
Vnt-PORTLAND
MIN
20.9100
15.9700
5. 3080
2.7220
2.5860
0.3572
53.2600
33.2400
20.0200
.
J V J.E
MAX
167.
81 .
90 .
62.
72.
2.
.
.
.
X5J.APIU
800
320
090
670
320
831
(LANE COLL
MAX
124
11 1
101
65
79
2
.700
.700
.800
.500
. 100
.932
.
.
(f* m n T f T* B C*
CTRL FIRE
MAX
216 .000
177 .
200.
91 .
169.
2 .
53.
33.
20.
100
200
300
200
445
260
240
020
STARTED
790924
800726
791006
791006
791006
.
.
.
-
STARTED
800825
800825
800825
800825
800825
.
.
f* ifป ซ \
STA )
STARTED
790924
80022 1
790924
790924
790924
82 1207
821207
821207 .
END
81
81
82
82
82
HMD
81
81
82
82
82
82
82
82
_DATE
0516
1212
1020
1020
1020
.
END_DA:
820306
811212
82020'
82020'
82020^
( i V "
0516
1212
120 1
120 1
120 1
1207
1207
1207
APPENDIX C
145
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTZCULATE NETWORK
NETWORK DATA SUMMARY
RATI015 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FIXE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
79
20
52
52
52
51
0
0
0
0
N
27
0
5
5
5
0
0
0
0
0
N
44
49
18
18
18
0
0
0
0
0
-3?u IUUUDMAU/ nAnr.
MEAN STD
68. 4089
67.6620
40.0562
24.7454
15.3110
0.5995
.
.
.
32.7162
37. 1958
16.2620
12. 1472
7.9269
0.0839
m
m
.
=390100068A07 NAME
MEAN
60. 1704
.
24.5580
16.5440
8.0140
.
.
.
.
STD
26.8842
.
4.7992
4.6353
2.4918
.
.
- r x i 1 <. a
MIN
30.6100
23. 1000
10.7600
7.7100
3.0500
0.3515
.
.
,
=PITT(U
MIN
21.01
.
17.66
11.83
5.49
.
.
.
.
MEAN
84.9300
75.7179
64.8783
31 . 1928
33.6856
.
.
.
.
f
;uuuฃAu/ nAnc.-rx.il
STD MIN
37.3448 14.060
32.5586
47.3925
22.31 18
41.0 173
.
.
.
.
.
7.612
28. 310
14.540
7.200
.
,
.
.
.
Ai.i.r.unr.n j
MAX
210.800
150.700
91 .770
76. 330
37.770
0.774
.
B
ALLEGHENY
MAX
143.80
.
29.20
23.71
1 1 .48
.
.
.
( t
A *
MAX
162.4
136 . 2
213.2
103.0
177 .9
.
.
.
f
.'
STARTED
810808
810808
811106
811106
81 1 106
.
t
f
/ป*% tt^^*tt\
CO H XG H 1 ~
STARTED
790819
790826
790826
790826
.
.
.
.
STARTED
800924
800924
820129
820 129
820129
.
.
f
END_DATE
821231
811212
821225
821225
821225
.
END_DAT
810609
821219
821219
821219
END_DA7
820417
810919
82 121 3
82 12 1 3
821213
.
146
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATIO 10
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATIO 10
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATIO 10
N
126
49
75
75
75
70
0
0
0
0
N
87
84
48
48
48
12
44
44
44
SITE =
MEAN
66.5377
52.9914
32.3801
19. 1360
13.2444
0.5447
.
.
.
= iS07807Z3AU 7 NAnE = BETHIiEHEn
STD MIN MAX
28.
21 .
14.
10.
7.
0.
.
.
.
5147
1 199
5525
0968
4137
1288
20. 1600
15.7100
6.7440
4. 1030
2.6410
0.2882
.
.
\
168.300
106. 100
63.700
45. 160
38.060
1 . 129
.
.
.
STARTED
801030
801030
810901
810901
810901
.
.
.
.
END
82
81
82
82
82
_DATE
1231
0326
1231
1231
1231
.
.
O-Lxฃป 3 7 O D 6 v
MEAN
98.9889
71 . 1432
38. 1283
22.0298
16.0979
0.4934
37.0945
24. 4895
12.6070
/ \r v \ i\
STD
49.
33.
17.
13.
7.
0.
19.
15.
7.
0
N MEAN
229 64.0732
531
107
107
107
70
36
36
36
35
52.5197
42 . 0201
24. 0924
17.9276
0.6575
34.7661
24.0761
10.6906
0 .4964
\J / JT.rt
9054
9890
9044
5122
5687
0948
3138
2823
3334
Vf ป MT*
J -3 t\V / JTttllC.
STD
26 . 0041
21 .
17 .
10 .
9 .
0.
12.
10.
4.
0.
8773
4055
7773
8482
1944
8830
6770
2008
0902
MIN MAX STARTED
31.3600 255.70 790813
24.6700
14.7000
7.8600
6.3300
0.3.109
10.6300
6.6300
3.0600
QUTT H ( Crtrt
- r HILA I ou U
MIN
13.4600
1 1 .8100
1 1 .2600
5.4700
3.6300
0. 1923
13.2400
7.5400
3.9600
0.3654
162.30
124. 10
94.20
37.51
0.62
127.20
105.00
36 .56
Sn n /\ H T\
BROAD
MAX
172. 100
151 .700
113. 800
69. 300
48. 300
1 .295
66.600
50.870
20. 150
0.757
800714
81 1031
811031
81 1031
.
820123
820123
820123
rป m ซ Tป r* nt ^
STREET )
STARTED
790424
790424
790424
790424
790424
820306
820306
820306
.
EHD
82
32
82
82
82
82
82
82
EHD_DA
8201 1 '
8205 17
8210 T-
82101'
8210 1(.
82 123
82123
32123
_DATI:
120 1
1201
120 1
120 ;
1201
.
1 125
1 125
1 125
APPENDIX C
147
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SJ.it,= ay / 1 HUUUiAD / rtAnt, = fttฑLA 1 3UU
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE 10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATIO 10
N
77
60
61
61
61
4
27
27
27
0
X
165
162
91
91
91
23
0
0
0
MEAN
58.9213
56.3255
39.7495
22.6802
17.0689
0.5491
33.2389
22.9381
10.3000
CTTTT OQ1
i>4- 1 t,- 39 i
MEAN
102.850
68.088
55.862
22.925
32.936
0.534
.
.
STD
24.0211
24.7122
12.6963
9.2448
7. 1762
0.0851
10.9477
9.6397
3.9554
STD
45.8658
28.7181
26.6761
1 1 .2859
21 .6809
0.2302
.
.
MIN
16.7400
22.0400
21.6000
6.7200
6.0300
0.4832
18.3900
10. 1 100
1 .3900
\f ซ M p o ปt T Y 11
NAnE-PHILA
MIN
17. 1800
12.3100
14.9300
5.0200
6.0600
0. 1382
,
.
.
S BKUAU
MAX
131.70
129.00
72.80
48.76
35.81
0.67
65.99
49.86
17.26
ar UU.L.J
STARTED
790804
800608
800510
800510
800510
.
820306
820306
820306
END_DAT
810227
81072V
8 2 1 0 2 '
82102C
82102C
8 2 1 0 2 '.,
32102'
82102
(ซ ป T .**ป ป*ปF*ป ^
ALL clj HEN I J
MAX STARTED
231.300 790503
207.000
128.300
79. 400
95.900
0.985
.
0 . .
, _ w _ CTfTtr*-"QQ*7ltlrtrt^rtJlrt*7 \TBMC* rป ซ* T T ป / Tป rป T *rst ปr in -r* -r T
H MEAN STD
36 46.4897 16.4976
0
36
36
36
33
0
0
0
0
.
39.6108
24.4307
15. 1796
0 .8923
.
.
.
,
.
14.8334
10.6616
5.9931
0 . 1 168
.
.
.
.
MIN
16.890
.
2. 389
1 . 125
1 .265
0.677
.
t
,
.
ijiiuni ro.ii
MAX
77.4900
.
69 .6200
45.7200
25.5100
1 . 1586
.
t
.
,
790503
790825
790825
790825
.
.
.
.
m Tป T> T> T ^
TฃH rL I -
STARTED
790608
.
7906 14
7906 14
790614
.
.
.
f
.
END_DATE
810227
810615
821 101
821 101
821 10 1
.
.
END_DA.
79100.
79100;
79 100i
79100,
APPENDIX C
148
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATI015 = DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE 10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
Sil
N
33
31
6
6
6
6
0
0
0
0
N
162
82
230
230
230
152
0
0
0
0
N
37
31
6
6
6
5
0
0
0
0
fฃ=iy / 1 4UU,
MEAN
77
53
58
31
27
1
.3027
.9748
.7467
.5633
. 1850
.0650
ซ
.
O T 4 f i A A '
MEAN
48. 4799
49
37
22
14
0
T f r*
.7796
.2296
.5610
.6677
.7891
.
> iT ฃ i ? / i *t v
MEAN
46.7224
40
46
26
20
1
.4839
. 2200
. 0683
.1517
.2721
.
.
,
,
S3AU /
STD
31 .
21 .
1 1 .
6.
6.
0.
.
.
.
> tl B f\ "7
* 4 A U /
STD
24.
22.
24.
14.
13.
0.
.
.
> t\ 1 t A
1 U i L A
STD
18.
13.
10 .
7.
3.
0.
.
.
.
f
HAHE
4462
7376
9919
5805
0075
1400
VI B M E*
ft An ฃ.
0529
1363
1537
8581
4408
2343
f\ "7 UN
U / MA
2 161
7457
3419
7736
6634
2917
-en
MIN
21 .
16.
42.
21 .
21 .
0.
.
.
.
J.LA I i
5500
9600
2900
2300
0600
8915
C. MA
MAX
167
1 16
77
40
37
1
1 & K .
.200
.600
.790
.570
.220
.315
.
,
.
D U T T R fijrtBปTLir'ปeซปT'
r H J. I* A \ Ti
MIN
10.8800
17.
1 .
0 .
0.
0.
.
MIN
14.
17.
30.
14.
16.
0.
.
.
f
7400
2060
7870
4190
1917
D U T T
r MIL A
4700
1000
7500
7200
0300
9613
w *v A n
MAX
139
133
166
99
1 1 1
2
MAX
87.
68 .
57.
34.
24.
1 .
.
.
f
m
Ltt\ .3 X
.000
.500
.000
.400
.800
.261
.
.
.
t* T f t
TZ Cv
4800
1300
9400
9900
3100
7121
LKฃ.Ai rj.; -
STARTED
7906 14
790626
790825
790825
790825
.
.
.
STOOHBT ^
STARTED
790503
80061 1
790527
790527
790527
.
.
STARTED
790509
790509
790825
790825
790825
f
.
END_DATE
790930
791003
790909
790909
790909
,
.
.
END_DATE
810227
810727
82 1020
82 1020
82 1020
.
END_DATE
79 1009
79 1009
790909
790909
790909
.
.
.
.
149
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15*DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COAP.SE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
a j. i t
N
164
80
162
162
162
1 14
0
0
0
0 .
N
40
0
38
38
38
37
0
0
0
0
N
0
0
13
13
13
0
0
0
0
0
= 3? i \ H v vac AW / nซnr. ^rn-Li. A i t-Kc.^o i i C.KฑAI
MEAN
56.6906
52.6752
42.8086
27.0371
15.7710
0.7407
.
.
.
- 7 Q *? i ti fl n
~ j 7 / 1 H U U
MEAN
51 .2712
.
45.7813
28.8089
16.9737
0.8999
.
.
STD
25.2107
21 .2627
22.0695
17.9600
7.9406
0. 1749
,
.
.
"3 "7 H ft "7 W ft M 17
o / A U / rl An t.
STD
19.6064
.
16.2191
12 . 4245
7.5851
0. 1084
.
f
,
MIN
11.1 100
17.4500
1 1 .6500
5.2900
0.8200
0.3616
m
.
.
D U T T R
- rnXLA
ซIN
18.0100
f
19.3600
10 . 1500
5.2000
0.6738
.
f
.
E=397140037A57 NAME=PHILA
MEAN
36.7935
21.5122
15.2814
.
.
.
.
. "
STD
15.8291
1 1 . 3340
5.6523
,
,
f
,
f
MIN
.
4.216
1 .908
2 . 308
.
.
.
.
.
MAX
152.900
125.400
140.900
123.300
45. 120
1 .355
B
.
.
STARTED
790521
8006 1 1
790521
790521
790521
,
f
t
f
END_DATE
810228
810727
820123
820123
820123
.
.
f
(TPMOT V TTVTTT7VBCTTV ^
TLnr Lr, Urii.vtRSJ.TlJ """
HAX STARTED
103.600
B
85.950
52.890
46.650
1.151
.
f
.
(TEMPLE UNIV
MAX
.
54.32
36 .59
21.18
,
.
.
.
790515
.
790515
790515
790515
.
,
.
^ XN T \
STARTED
790602
790602
790602
.
.
f
.
f
END_DATE
790930
.
790930
790930
790930
.
.
.
END_DATE
79093C
790930
790930
.
.
150
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
5
N
172
179
86
86
86
19
0
0
0
0
N
108
0
142
142
142
94
0
0
0
0
N
0
27
74
74
74
0
0
0
0
0
xTE=.sy / i HO UJOAU / si An.c. = r fix.L A lar \jvnn UAUJIJ. xui ;
MEAN STD MIN MAX STARTED
64.2967 30.6092 21.3000 189.600 790527
56.0651 28.2462 12.3100 165.700 790527
44.9258 38.2699 13.2900 323.900 790825
24.4470 18.0912 7.1700 140.500 790825
20.4783 33.2053 0.9000 308.500 790825
0.8092 0.1085 0.6239 1.078
.
C T T T* ^ Q "7 ^
Ollt---i7/Z
MEAN
91 .2123
,
57. 1342
34.3022
22.8307
0.6053
.
t
.
CTTP (1 1 rt ^ rt A
SiTE- 4 1 U JU U
MEAN
34.2307
25. 1492
14.5818
10.5676
.
.
,
.
.
1mft"ป VTRMP OTT*T fl4S7TTl!nAl
_ _ . . A U / nAnJc,-rJ.Tl lnAฃiฃ*LWUUJ
STD MIN MAX
44.1537 26.4900 354.700
26.8045 10.5400 181.100
16.4516 7.2100 121 .500
14.3469 3.3300 88.700
0.1228 0.3491 1.175
.
STD MIN MAX
11 .9523 18.110 66.70
11.8046 6.720 65.94
7.3657 4.660 41.53
6.5170 1 .883 35.57
.
-
. .
.
STARTED
791 11 1
.
790813
790813
790813
.
.
,
.
* ซ ป ^ *ป >
1 F LIB i
STARTED
810709
8107 15
810715
810715
.
.
.
.
.
END_DATE
810227
810615
821 10 1
821101
821101
.
END_DATE
821231
.
821225
821225
821225
.
.
.
,
END_DA
T
81 1224
82121
82121
82121
.
g
9
a
.
151
APPENDIX C
-------
EXVIRONHENTAL PROTECTIOK AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE 15
RATI015
DICHOT10
FINE10
COARSE10
RATIO 10
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
5.
N
0
8
54
54
54
0
0
0
0
1 T t = H ฃ 0 3 O U U t,
MEAN
39.0537
26.7433
15.0836
1 1.6597
.
.
.
.
i iAU / ซซn
STD
9.84100
8.88747
6.37528
4.81072
.
.
.
,
r. = t.nAKLtai
MIN
28.410
6.567
4.290
1. 163
.
,
f
f
0 . .
_. CTTIT tillrt^flflf^Aฃ*rt*7 vtปi*ซป,/ปt*ซmfiiปvr
N MEAN
32 79.7812
30
3
3
3
3
0
0
0
0
N
91
49
63
63
63
41
0
0
0
0
57.8463
28.4533
18.2433
10.2100
0.5620
.
.
.
1 U OH U / flM
STD
28. 1024
22.8831
6.7163
7.8726
6. 1478
0. 1203
.
.
.
-
MIN
38. 1900
26.9100
24. 1200
9.2200
3.2500
0.4235
.
.
.
UN Sl~ ir.LKl
MAX
55.46
43.59
32.65
20.58
.
.
.
.
f\ f\ f* H flT^fP
OOu A I WD t,r
MAX
172.500
137.700
36. 190
23.710
14.900
0.641
.
.
.
-
SITE=442540006A07 NAME=NASHVILLE (8TH AVI
MEAN
75.2157
58.2278
36 .8992
21 .8944
15.0049
0.4790
.
.
.
,
STD
24.1621
16.9203
15.5275
10.7930
10.9473
0. 1 145
.
.
.
,
MIN
25.5500
14.5100
10 .5500
5.5800
1.5100
0. 1762
.
.
.
.
MAX
139 . 200
92.720
75.780
52.830
54.830
0.675
.
.
.
.
: si*;
STARTED
81 1025
811019
811019
811019
.
.
.
.
** T" n ^
STARTED
800924
800924
811013
811013
811013
.
.
.
f. \t || IF. \
iNU ฃ )
STARTED
800930
800930
811001
811001
811001
.
.
.
.
END_DATE
81 1206
821207
821207
821207
.
.
END_DATE
81 1025
810428
81 1025
81 1025
81 1025
.
,
.
END_DATE
821225
810913
821231
821231
821231
.
.
.
152
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO 15ซDICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COAP.SE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FIKE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
- ij.
N
105
90
132
132
132
82
0
0
0
0
N
76
67
90
90
90
49
5
5
5
5
N
140
0
140
140
140
129
0
0
0
0
Iฃ = 43 1 J 1 UU3UAU / ft
MEAN STD
75.9445
57.8864
37.2097
18.7594
18.4502
0.5320
.
.
.
47.2768
34. 1261
14.3147
8.3235
10.6466
0. 1495
.
.
T T t* ti C 1 *7 ft ft ft rt ^ JlftT
i T E 4 O i /UUvU^AU /
MEAN STD
128.056
98.706
69.005
22.539
46.469
0.535
58.342
27.652
30. 670
0. 432
- SITE=45
MEAN
83.8057
.
51 .8665
13.2784
38.5888
0.6307
.
.
.
m
60.6644
57.4000
45.4747
21 .3363
31 .4214
0.2081
44. 1079
19. 6839
26.6825
0 . 0829
1710004A07
STD
46.7220
.
29. 1638
6.5881
26. 1443
0. 1558
.
.
.
MIN
19.2300
10.5500
9.0960
5.8800
0.8100
0.2509
.
.
.
U * M T* Y* T VAC
JiAnt- t.L r A;
MIN
30. 1300
26.2000
16.9100
4.8800
4.8200
0. 1496
1 1 .7900
6.4700
3.6600
0.3314
NAME=EL
MIN
6.40300
6 . 05800
2 . 34000
1 .77000
0. 14982
.
f
f
t
MAX STARTED
458.800
304.400
92.080
60.910
74. 940
1.255
.
.
.
MAX
333.600
260.900
297.600
147.700
211 .500
1 . 361
121 . 300
47 .800
73. 400
0.550
PASO (CLINT
MAX
259.40
181 . 30
34. 00
150.30
1 . 38
.
.
.
.
8001 16
8001 16
8001 16
8001 16
8001 16
.
.
.
STARTED
791 123
791 123
791205
791205
791205
.
821201
821201
821201
) . .
STARTED
791 1 17
791117
791117
791 1 17
.
m
.
.
END_DATE
820505
811019
821026
821026
821026
.
.
.
.
END_DATE
821231
811212
821 125
821 125
821 125
821231
82 1231
821231
END_DA.Tฃ
82 1008
820920
820920
820920
.
.
f
.
.
153
APPENDIX C
-------
RATIO 15
ENVIRONMENTAL PROTECTION AGENCY
IKHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
DICHOT15/HIVOL RATIO 1 0 = DICHOT 1 0/HIVOL
SAMPLER
TSP
SSI
DICHOT1S
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FIHE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
N
59
0
41
41
41
36
0
0
0
0
N
87
80
13
13
13
10
16
16
16
13
N
64
8
55
55
55
<41
0
0
0
0
- 51Ti=43i
MEAN
63.7066
,
36.5246
16.8989
19.6253
0.5982
.
.
.
33UU14AU /
STD
25.4750
.
15.0838
7.3071
1 1 .8857
0.2699
.
.
.
- SITE=452560034A07
MEAN
99.2163
74.9887
US. 86>46
20.3646
25.5000
0.14710
37.6700
16.2881
21 . 3831
0 . 3940
SITE=4547
MEAN
62.2014
44.8025
35. 1627
16.5111
18.6516
0.5962
.
.
.
f
STD
36. 1416
25. 1468
18.241 1
18. 1541
10.8579
0.0697
10.5752
7.0784
7.2363
0.0850
15001A07
STD
32.8293
18.6880
16.0624
9.6983
10.4026
0.2147
.
.
,
.
rtAnt=nuu:
nix
5.21200
.
7.24000
4.86300
2.37700
0.31829
.
a
,
-
>TUJt V UAn^-
MAX
125.800
.
74.600
39.970
59.690
1 .501
.
.
.
NAME=HOUSTON (CAMS-
HIN
30.0900
26.6800
25.3900
9.5800
10.0300
0.3473
24.7400
4.5400
10.0900
0.2342
MAX
203.400
140 .700
88.570
78.440
42.990
0.573
61 .480
33.470
33.730
0.525
NAME=HOUSTON (SEABRO
MIN
15. 0800
24.4500
12.5800
4.7400
4.7700
0.2292
,
.
.
.
MAX
171 . 900
70. 100
80 . 980
44 . 540
54.020
1 . 135
.
.
.
.
STARTED
791205
79121 1
791211
79121 1
.
.
.
.
'
STARTED
791123
791 129
820324
820324
820324
.
820324
820324
820324
STARTED
791129
810609
791 129
791129
791129
.
.
.
.
,
END_DATE
820312
.
820312
820312
820312
.
.
,
,
END_DATE
821231
821231
820914
8209 14
820914
.
820902
820902
820902
END_DATE
821231
810820
821219
821219
821219
.
.
.
.
154
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
5iX
N
121
75
46
46
46
38
5
5
5
5
N
127
71
62
62
62
59
3
3
3
2
N
72
62
0
0
0
0
0
0
0
0
MEAN
67.2394
56.5584
36.3620
15.5265
20.8348
0.6157
34. 1380
22.3040
1 1 .8340
0.5631
ItiftQOArtA
-40U"iUUU
MEAN
75.4173
69.6396
39. 1019
17.4992
21 .6026
0.6121
44. 1367
32 . 0233
12. 1 133
0. 6704
MEAN
53.2967
44.8774
,
t
.
,
f
r
t
UIAU/ rtAni = nAijJiA IB
STD MIN
38.3620
33.3769
21 .4810
15.4139
1 1 . 9440
0. 1227
17.6310
13.3101
5.3987
0.1211
1 H ft "7 MUMP
1 A v / It AH I*
STD
38.6250
36.2693
15.9770
9.4525
10.7197
0. 1023
31 . 19-09
24.2079
6 .9886
18.7300
18. 1 100
11 .9800
3.8600
6. 1700
0. 3738
12. 1800
7.5000
3. 6700
0.4235
C 1 T T TBI<*P
- o A 1* 1 LAKC.
MIN
22.8100
27. 1500
15.5700
5.9300
6.3400
0.2083
19.7400
13.3000
6.4400
0.1383 0.5727
A<*flBA*7 IkfTIMP IDTTIJfT
UZUAU/ NArlr.-AK.LXn.GT
STD MIN
18.4520 ,20.76
17.9635
.
.
.
.
.
,
.
18. 32
.
.
.
.
t
m
,
KUUKSAfllS
MAX
262.800
213.900
96.560
79.030
59.990
1 .078
51 .340
34.440
17 .940
0.665
H T T V f f\. *
U JL 1 I I O ป
MAX
255.000
207.600
97. 170
52 .980
68.890
0.797
79 .280
59 .360
19 .920
0 .768
(f* f\ M M
conn
MAX
103.0
110.2
.
.
.
.
STARTED
800714
800714
810913
810913
810913
.
821 125
821 125
821 125
STARTED
800714
800714
810721
810721
810721
.
821125
821 125
821 125
W * ป* f* \
HLDG ) -
STARTED
800831
800831
.
.
.
t
.
END_DATE
821231
811212
821 1 19
821 119
821 1 19
,
821219
821219
821219
END_DATE
821213
811212
821 1 19
821 1 19
821 1 19
.
821225
821225
821225
END_DATE
81 1230
811130
.
m
,
.
.
155
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FIHE15
COAP.SE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
- SJ.1 i=MO 1 ป tU UU3AU / l\Hni.-
N MEAN STD
67 51.2549 20.665
67 40.3370 17.859
0
0
0
0
0
0
0
0
nunr iun
MIN
21 .57
16.43
*_ U ^ TS ^ป T ป T
N MEAN STD MIN
122 70.0369 25.6832 25.6000
46
122
122
122
1 13
0
0
0
54.0367
38.9171
20.8599
18.0578
0.5565
.
.
0
N MEAN
123
43
78
78
78
66
0
0
0
0
58.4980
49.8451
34.8124
19 .5500
15.2627
0.6008
.
.
. t
m
20.
17.
12.
9.
0.
.
.
.
f\ *7 ft rt *T
4712 22.2700
3304 1
7192
8043
1 186
vr M T* _
0 / A 0 / n*riฃ,-
STD
22
22
14
9
9
0
.3138
.5644
.6312
.3013
.9341
. 1057
.
.
.
.
2.7100
6.9600
2.3100
0.3301
.
.
.
\t f\ D V f\ T V
NOKr ULK
MIN
23.270
19.510
12.540
5.630
0.610
0. 315
.
,
.
,
I V J.K
MAX
106
94
MAX
149
102
126
108
66
1
(n T n
OLD
MAX
128
1 17
87
45
68
0
UJ.AJ. A
.90
.04
.700
.400
.400
.900
. 120
. 193
.
.
.
STARTED
800924
800924
__ _.
STARTED
800831
80083
80083
80083
80083
1
1
1
1
,
.
.
.
END_DATE
811212
81 1 130
END_DATE
821020
81072
82101
82101
82101
1
4
4
4
.
^ rt M T \1 T" rt \I 11 ^
DOniJilUN U I -
STARTED
.400
.500
.640
. 020
. 480
.965
.
,
.
,
80092
80092
81081
81081
81081
4
4
4
4
4
.
9
.
.
f
END_DATE
82 123
81072
82123
82 123
82123
1
1
1
1
1
.
.
.
.
156
APPENDIX C
-------
SAMPLER
SAMPLER
RATI015
ENVIRONMENTAL PROTECTIOM AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
'DICHOT15/HIVOL RATIO 10 = DICHOT 1 0/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
;
N
1 14
31
109
109
109
100
0
0
0
0
>XTES14020 JUOU 1 AU / ft AH t = f A X ttf J
MEAN STD MIN
44.
44.
28.
19.
8.
0.
.
.
.
.
0743
2365
1021
5425
5587
6096
13.
14.
12.
10.
4.
0.
.
.
,
t
4277
1 196
0059
0501
4482
1062
18
21
9
5
1
0
.5600
.8100
.2370
.5480
.4900
.3405
.
.
.
IX ^ to
MAX
79.
81 .
66.
49.
23.
0.
.
.
.
.
STARTED
3300
3200
2800
6000
9300
9676
800831
800831
800831
800831
800831
.
.
.
.
END_DATE
82
81
82
82
82
1101
0814
1231
1231
1231
.
.
.
.
.
SITE=482660002A07
N
MEAN
STD
MIN
VA (HEALTH DEPT )
MAX STARTED
END DAT!
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COAP.SE10
RATI010
24 57.1817 19.3338 36.23 116.60 800906
22 43.7655 16.4336 23.45 86.74 800831
0 . . .
0 . . .
0 . . .
0 . . .
0 . . . .
0 . . . .
0 . . . .
0 . . .
810209
810209
.
.
SITE=491840057A07
NAME'
MEAN
STD
MIN
(DUUAMISH
MAX
STARTED
END_DATE
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
121
16
1 1 1
1 1 1
1 1 1
108
2
2
2
2
96
57
39
15
24
0
56
42
13
0
. 6955
. 1800
.8265
.4980
. 3290
. 4094
. 6800
.8750
.8050
.8222
52
24
21
10
15
0
47
42
5
0
.5771
.9435
. 4984
.2881
.0926
.0796
.5741
.5183
.0558
.4773
28
34
9
4
2
0
23
12
10
0
.0100
.4000
. 3540
.4510
.4620
.2138
.0400
.8100
.2300
.4847
408.
100 .
1 19.
53.
89.
0 .
90 .
72.
17.
1 .
900
300
300
650
500
615
320
940
380
160
80
81
80
80
80
82
82
82
1217
0203
1217
1217
1217
1219
1219
1219
m
821231
810709
821213
821213
821213
821231
821231
821231
157
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICIPATE NETWORK
NETWORK DATA SUMMARY
RATIO15=DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE 15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE10
COARSE10
RATI010
N
0
6
79
79
79
0
3
3
3
0
N
95
0
143
143
143
92
0
0
0
0
N
73
25
96
96
96
53
0
0
0
0
>ITE=4ป 1841
MEAN
.
50. 1067
36.7344
14.8762
21 .8586
.
33.7900
26.7100
7.0800
IDS /AS / It
STD
.
18.4129
18.8889
8.9137
13.2840
.
21.6347
21 .5715
0.5966
MIN
.
26.20
11.14
4.30
4.08
.
17.39
10.88
6.51
*El UUWAnii
MAX
^
82.05
98.05
52.73
61 .59
.
58.31
51.28
7.70
n uui,;
STARTED
m
810627
810627
810627
810627
821219
821219
821219
END_DATE
.
810727
821213
821213
821213
821231
821231
82123 1
MEAN
43.7171
.
20.2465
14.4772
5.7688
0 .5441
.
.
.
CTTV (iQ^Af
5-lTE lr"*U1
MEAM
89. 1262
68. 0870
41 .7349
13.541 1
28. 1949
0.5130
.
f
.
.
; i 3 H v / JTA
STD
20.9732
.
12.5577
10.0691
6.2721
0.2177
.
.
.
STD
47.5455
36.8191
24.7642
1 1 .5526
20.7939
0. 1968
,
,
.
.
1 1 C, - i E. A i i Jut
MIN
9.26700
.
3.58900
3.09300
0. 10500
0. 13147
ป
,
%
MIN
14.5500
7.3740
5.4900
2 . 0700
3. 2800
0.3077
.
.
.
f
. {\*ฑii L.j.uni uu >
MAX STARTED
110.100 790930
^
72.510
50. 120
25.370
1 .204
.
.
MAX
247 . 900
166.800
120.700
53. 320
103. 000
1 .727
.
f
.
f
f
790930
790930
790930
.
.
.
** T* ^
ST J
STARTED
800831
800831
801105
801 105
80 1 105
.
.
.
t
END_DATE
810528
820330
820330
820330
.
.
.
END_DATE
821219
810227
82 1219
821219
821219
.
.
.
.
158
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALA3LE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO15*DICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
SSI
DICHOT15
FINE15
COARSE15
RATI015
DICHOT10
FINE 10
COARSE10
RATI010
SAMPLER
TSP
SSI
DICHOT
FINE15
COARSE
RATI01
DICHOT
FINE10
COARSE
RATI01
15
15
5
10
10
0
SAMPLER
TSP
SSI
DICHOT
FINE15
COARSE
RATI01
15
15
5
DICHOT10
FINE10
COARSE
RATI01
10
0
5il
N
0
0
61
61
61
0
0
0
0
0
N
70
0
68
68
68
60
0
0-
0
0
N
86
41
49
49
49
35
0
0
0
0
MEAN
39
21
17
f
.2267
.951 1
.2751
.
.
.
.
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821107
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f
159
APPENDIX C
-------
ENVIRONMENTAL PROTECTION AGENCY
INHALABLE PARTICULATE NETWORK
NETWORK DATA SUMMARY
RATIO1SปDICHOT15/HIVOL RATIO 10 = DICHOT10/HIVOL
SAMPLER
TSP
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FINE 15
COARSE15
RATI015
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APPENDIX F
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