EPA/600/R-96/033
March, 1996
Guidance for Total Organics
Final Report
By:
Robert F. Martz
Radian Corporation
P.O. Box 13000
Research Triangle Park, North Carolina 27709
Contract Number 68-D4-0022
Work Assignment No. 08
Prepared for:
Easter A. Coppedge and Larry D. Johnson
National Exposure Research Laboratory
Air Measurements Research Division
Methods Branch
U. S. Environmental Protection Agency
Research Triangle Park, North Carolina 27711
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Disclaimer
The information in this document has been funded wholly or in part by the United States
Environmental Protection Agency under EPA Contract 68-D4-0022 to Radian Corporation. It
has been subjected to Agency review and approved for publication. Mention of trade names or
commercial products does not constitute endorsement or recommendation for use.
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Abstract
This document provides guidance to those wishing to determine the total organics content
of source samples. Writers of air quality permit applications for waste combustion units require
total organics data for their assessments. This document identifies specific techniques to
determine the total organics sampled from stationary sources. It describes the measurement of
total organics from stack emissions and related field sampling efforts, combining the organics
from three specific boiling point/vapor pressure classes: light hydrocarbons and volatile organics
(boiling points <100°C), semivolatile organics (boiling points 100°C to 300°C), and non-volatile
organics (boiling points >300°C). It describes methods for measuring and reporting the individual
parameters. The document seeks to avoid the confusion about organics measurement and
eliminate the misleading and non-descriptive titles often given to different facets of organics
analysis. It also provides information about combining the component parts of the organics
analysis results into a helpful description of the data. Knowing the amount of previously
uncharacterized organic material enables more accurate risk assessment estimates to be made.
Discussions of the specific methods and operating procedures are found in the appendices and
references.
in
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Contents
Disclaimer ii
Abstract iii
Acknowledgments vii
Glossary of Terms viii
1 Introduction/Background 1
2 Method for Total Organics Measurement 4
3 Field Gas Chromatography (Field GC) Method and
Purge and Trap GC Method 6
4 Source Sampling and Sample Extract Preparation
for TCO and GRAY 10
5 Total Chromatographic Organic (TCO) Method 12
6 Gravimetric (GRAY) Method 14
References 16
Appendices
A. Recommended Operating Procedure for Field Gas Chromatography
B. Recommended Operating Procedure for Purge and Trap GC
C. Recommended Operating Procedure for Total Chromatographable Organics
(TCO) Analysis
D. Recommended Operating Procedure for Gravimetric (GRAY) Analysis of Organic
Extracts
IV
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Contents, Continued
E. EPA Draft Method 0040 - Sampling of Principal Organic Hazardous Constituents
from Combustion Sources Using Tedlar® Bags
F. SW-846, Method 0010 - Modified Method 5 Sampling Train
G. Method 3542 - Extraction of Semivolatile Analytes Collected Using the Modified
Method 5 (Method 0010) Train
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List of Tables
Total Organics Components
List of Figures
Stationary Source Emissions
VI
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Acknowledgments
This document was prepared for the US Environmental Protection Agency's National
Exposure Research Laboratory (NERL) located in the Research Triangle Park, NC. The authors
wish to thank those people who have made this work possible: Joan T. Bursey and Raymond G.
Merrill of Radian Corporation, and Larry D. Johnson of EPA.
vn
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Acronyms and Abbreviations
AREAL - Atmospheric Research and Exposure Assessment Laboratory, RTF
AEERL - Air and Energy Engineering Research Laboratory, RTF
CH4 - Methane
C7 - Heptane
C17 - Heptadecane
Draft Method 0040 - "Sampling of Principal Organic Hazardous Constituents from
Combustion Sources Using Tedlar® Bags"
Draft Method 3542 - "Extraction of Semivolatile Analytes Collected Using Modified
Method 5 (Method 0010) Train"
EPA - Environmental Protection Agency
FID - Flame ionization detector
Field GC - Field gas chromatography, light organics collected in Tedlar® bags and
analyzed in the field by GC/FID
GC - Gas chromatograph
GRAV - Gravimetric mass, nonvolatile organics with boiling point > 300°C
heptane - Straight chain hydrocarbon, saturated, 7 carbon atoms
heptadecane - Straight chain hydrocarbon, saturated, 17 carbon atoms
Level 1 - IERL (AEERL) Procedures Manual: Level 1 Environmental Assessment
m - Meter
Method 8270 - "SW-846, Method 8270, Gas Chromatography/Mass Spectrometry for
Semivolatile Organics: Capillary Column Technique"
viii
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Acronyms and Abbreviations, Continued
Method 0010 - "SW-846, Method 0010, Modified Method 5 Sampling Train"
mL - Milliliter
ug - Microgram
uL - Microliter
m3 - Cubic meter
MS - Mass spectrometry
purge and trap - Analytical technique where the water sample is introduced to the
instrument by gas purging, trapping of the gas, and desorption from the trap
QC - Quality control
RCRA - Resource Conservation and Recovery Act
Recoverable organics - Those organic compounds capable of being collected in a specific
sampling train (Method 0010, Draft Method 0040) and subsequently analyzed.
RTF - Research Triangle Park, North Carolina
semivolatile - Compound class between the volatile and non volatile compounds, generally
defined by boiling point between 100°C and 300°C.
SW-846 - Test Methods for Evaluating Solid Waste, Physical/Chemical Methods, SW-846
Manual, 3rd Edition.
Tedlar® - Trade name for sampling bag material used in direct collection of air samples
total organics - Combination of Field GC, TCO, and GRAY mass
TCO - Total chromatographable organics
volatiles - Volatile organic compounds with boiling points < 100°C
ix
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Section 1
Introduction/Background
The characterization of stationary source emissions requires screening and analysis
procedures that identify components of several compound classes. The need to characterize
emissions containing multiple organic compounds continues to increase. Revisions to the
guidance for conducting risk assessments at Resource Conservation and Recovery Act (RCRA)
hazardous waste combustion units have recently included the requirement that total organic
carbon analysis be conducted.1'2 The portion of organic emissions that have not been specifically
identified and quantified by other methods must be measured. By knowing the amounts of
previously uncharacterized organic material, more accurate risk assessment estimates can be
made. Writers of air quality permit applications for waste combustion units require total organics
data for their assessments. This document identifies specific techniques to determine the total
organics sampled from stationary sources.
This document describes the measurement of total organics from stack emissions and
related field sampling efforts, combining the organics from three specific boiling point/vapor
pressure classes: light hydrocarbons and volatile organics, semivolatile organics, and nonvolatile
organic compounds. The total organics measurements are not merely a mass measurement of
carbon, soot, or particulate content alone. Total organics in this case combines the low boiling
point organic compounds (Field GC and Purge & Trap GC) with the organic compounds with
boiling points greater than heptane (TCO and GRAY) collected with a Method 0010 sampling
train. The combination of the three fractions and techniques gives the analyst specific identified
organic compound classes and provides the means to analyze the components of each boiling
point class. The sampling and analytical information necessary to characterize the full boiling
point range of organic material encountered in source emissions is provided in this document.
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Field gas chromatography (Field GC) with flame ionization detection (FID) of an
integrated Tedlar® bag sample is recommended for organics of boiling points less than 100°C.
Total chromatographable organic (TCO) analysis is recommended for compounds boiling
between 100°C and 300°C. Finally, gravimetric (GRAY) techniques are appropriate for
compounds boiling at 300° C or higher. The total organics are the sum of volatile organic
compounds (VOC), TCO, and GRAY. The summary of these three techniques is shown in Figure
1.
Total organic carbon in this document refers to the volatile organics (boiling point <
100°C) from a field GC and purge and trap GC measurement combined with organics of boiling
point > 100°C collected in a Method 0010 sampling train. The combination of two sampling and
three analytical techniques gives the investigator the approximate mass of all identified and
unidentified "recoverable" organic material. The mass of organic material that remains after
correction for the identified organic compounds found using RCRA SW-846 methods is the
residual organic carbon and this quantity is used to estimate risk from unidentified organic
emissions. A description of the measurement techniques is found in the following pages. Detailed
discussions of methods and operating procedures are found in the references and appendices of
this document.
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Stationary
Source Emissions
Analysis: Field GC/FID for bag
Purge & Trap GC/FID
for condensate
100°C-300°CBP
Sampling: Method 0010
Analysis: TCO GC/FID
Figure 1. Stationary Source Emissions
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Section 2
Method for Total Organics Measurement
The method for total organics measurement incorporates three distinct sets of analyses,
described in the following sections:
First, the light organics are collected and measured by a technique known as Field
GC using bag sampling according to Draft Method 0040. Emphasis is made on the
identification of methane, because methane may appear in significant quantities in
stack sampling efforts and correct identification may be vital to subsequent analysis
of risk assessment of the stationary source. In addition, the light organics
collected in the condensate trap of Draft Method 0040 are analyzed by Purge and
Trap GC/FID.
Second, Method 0010 samples are collected and the extracts of the train
components are analyzed. The 100°C to 300°C organic compounds, TCO, are
determined by GC/FID of the dichloromethane extracts of the pooled components
of the sampling train. C7 and C17 are used as marker compounds because their
boiling points are 98 °C and 302°C, respectively.
Finally, the 300°C and higher boiling organics, non-volatile organics, are
determined by a gravimetric procedure known as GRAY from the same pooled
dichloromethane extract of the train components as the TCO procedure.
The data from these three analytical determinations are collected and added to obtain a
total organics value for the sample of choice, as shown in Table 1. The value provides a
benchmark of total organic content for specific identification of individual compounds, necessary
for emission and/or risk assessment calculations. The total value is then comparable from site to
site or application to application, and the end-user or researcher can more easily compare total
organics data from various sources.
The three analysis components allow the reviewer of the data to keep track of the total
organics in a material balance manner. The individual boiling point ranges allow identification of
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organic compounds by defined classes and assist in the estimate of completeness of
characterization. This identification of known vs. unidentified organics is of benefit in subsequent
risk assessment calculations.
Table 1. Total Organics Components
Component
Field GC, volatile
organics
TCO, semivolatile
organics
GRAY,
non-volatile
organics
Method
Sampling
0040
0010
0010
Analysis
GC/FID and
Purge & Trap
GC/FID
GC/FID
gravimetric
Units
|ig/m3
|ig/m3
|ig/m3
Boiling Point
Range
< 100°C
100° C
300°C
Vapor Pressure
> 40 mm at
22.3°C
(> heptane)
1 mm Hg at
115°C
>VP>
40 mm at 22.3 °C
< 1 mm Hg at
115°C
(< heptadecane)
Total Organics = (Field GC + Purge and trap GC) + TCO + GRAY in units of |ig/m3
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Section 3
Field Gas Chromatography (Field GC) Method and
Purge and Trap GC Method
The field GC portion of total organics is determined by field analysis of a bag sample by
GC with a flame ionization detector (FID). This procedure is described in this document as
Appendix A and in EPA Draft Method 0040 (Appendix E). The identified range of organics for
field GC is defined by boiling point range, in this case < 100° C. The analysis procedures are
normally performed in the field to minimize sample (compound) loss due to storage and shipping.
Additionally, the condensate collected as a part of the bag sampling is analyzed for low boiling
organics by purge and trap GC/FID. The condensate fraction is normally transferred to a vial
with no headspace and shipped to the laboratory for analysis.
Bag Sampling/Analysis
Compounds with boiling points below 100°C are sampled into Tedlar® bags and require
on site gas chromatographic analysis of the collected sample. The operating procedure for this
methodology is included in this document as Appendix A and Draft Method 0040. The range of
applicable compounds is very large: methane has a boiling point of-160°C, and hexane boils at
69°C. The reporting range for the methodology extends to 100°C. If a packed column is used to
perform all of the gas chromatographic analysis, a very judicious selection of phase and analytical
conditions must be made in order to achieve chromatographic resolution for methane at the same
time as the total analysis time is limited to no more than 15-20 minutes. Some investigators prefer
the use of two gas chromatographs, one with an appropriate column and conditions for Cx - C4
and the second with an appropriate column and conditions for the C4 - C6 range. A capillary
column is required to perform the analysis over the entire volatility range with adequate
resolution. A capillary column with a length of 60 m may be required to provide adequate
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resolution for the C2-hydrocarbon isomers. The gas chromatographic analysis will primarily be
separating compounds on the basis of boiling points, but the separation will also be influenced by
the polarity of the compounds in some cases. Numerous chromatographic conditions such as
column temperature, ramp for temperature programming, duration of an isothermal hold, and
temperature of any transfer line will all have to be optimized for the best chromatographic results.
A flame ionization detector is required to perform the analysis.
The gas chromatograph must be calibrated for quantitative analysis with a normal
hydrocarbon curve. The curve is prepared using certified cylinders containing the n-alkanes from
Cj through C6. A multipoint calibration of at least three points (in duplicate) is required.
Calibration for methane (CH4) must be performed carefully so that the quantity of methane can be
determined accurately. Methane is often found in significant quantities when incinerator stacks
are sampled, and it is essential to be able to identify the compound correctly and provide an
accurate quantitative measurement when calculations of risk or regulatory significance are being
performed. The certified Cl - C6 standard gas mixture is used to calibrate the field gas
chromatograph and a point approximately in the middle of the calibration range should be
analyzed at least once per day as a calibration check. The multipoint calibration is achieved either
through the use of multiple cylinders at different concentrations or by the use of sample loops of
varying sizes.
After full calibration, sample analysis is initiated when the sample container (the Tedlar®
bag) is connected to the sampling valve and the sample gas is drawn through the valve and sample
loop. When the valve is sufficiently purged, the valve is actuated and the contents of the loop are
injected into the chromatograph. Simultaneously with the injection of the sample, the temperature
programmer and integrator/data system data acquisition are started. Chromatograms and
integrator/data system output are collected. Retention times and responses must agree to within 5
percent relative standard deviation with the calibration curve. Uniform FID response for varying
compound classes is assumed in this methodology. The resulting quantitative results therefore
tend to be biased low for compounds which are not n-alkanes. In many, if not most, cases the
species present are not identical to those used for calibration of the on-site chromatograph; an
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exact correspondence between standard peaks and the peaks observed in the sample
chromatogram will not be achieved.
Purge and Trap Sampling/Analysis
Compounds with boiling points below 100°C are sampled by Draft Method 0040 into the
condensate ahead of the Tedlar® bag. The operating procedure for this methodology is included
in this document as Appendix B. This condensate requires purge and trap gas chromatographic
analysis of the collected water sample. A gas chromatograph with an appropriate column and
conditions for the C5 - C7 range is required. A capillary column with a length of 60 m may be
required to provide adequate resolution for smaller organic and hydrocarbon isomers. A flame
ionization detector is required to perform this analysis.
The purge and trap GC must be calibrated for quantitative analysis with a normal
hydrocarbon curve. The curve is prepared using liquid alkane standards containing the n-alkanes
from C5 through C7. A multipoint calibration of at least three points (in duplicate) is required.
The alkane mixture is used to calibrate the GC and a point approximately in the middle of the
calibration range should be analyzed at least once per day as a calibration check. The multipoint
calibration is achieved through the use of serial dilutions of the primary stock standard mixture in
methanol solution.
After full calibration, sample analysis is initiated when an aliquot of the water sample in
the VOA vial is transferred to the purge flask. The purge gas is actuated, purging the vapor with
an inert gas to the sorbent trap (VOCOL®, VOCARB®, or equivalent). When the sample is
sufficiently purged from the vessel into the trap, the valve is actuated and the trap contents are
desorbed by rapid heating onto the head of the GC column with the FID detector. The
temperature programmer and integrator/data system data acquisition are started. Chromatograms
and integrator/data system output are collected. Uniform FID response for varying compound
classes is assumed in this methodology. Compounds found with retention times prior to the C4
retention time are quantified with an appropriate response factor and the value reported as C4 with
the other organic results.
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Section 4
Source Sampling and Sample Extract Preparation for TCO and GRAV
In order to obtain the sample required for TCO and GRAV analysis, the field sample must
be collected in the appropriate manner. The sample is collected using the Semivolatile Organic
Sampling Train, Method 0010, included in this document as Appendix F. This sampling method,
also known as the Modified Method 5 Sampling Train, generates a set of sampling train
components which must be carefully handled in order to preserve the compounds of interest.
The sampling train is disassembled and "broken-down" according to the specifications of
Draft Method 3542, "Extraction of Semivolatile Analytes Collected Using Modified Method 5
(Method 0010) Train (Appendix G). There are, however, several exceptions to the method as
written which must be observed in order to obtain valid data for total organics determinations.
They are listed below:
The component parts of the sampling train are normally collected in three parts: 1)
particulate matter filter and front half rinse, 2) condensate and condensate rinse,
and 3) XAD-2® and back half rinse. These components are combined into a single
pooled extract for the purposes of total organics measurements. As in Method
3542, the three parts may be taken to final volumes of 5 mL each, but the three
extracts are then combined and taken to a final pooled volume of no less than 5
mL. Note: At no time should any of the extracts (parts or pooled) be reduced to
volumes less than 3 mL, or loss of Semivolatile compounds may occur.
Since the extracts for total organics determinations are analyzed by GC/FID and
gravimetric techniques, none of the surrogates, isotopically-labeled standards, or
internal standards associated with GC/MS analysis (Method 8270) should be
added to the extractors or sample extracts. After the sampling train is
disassembled, the components are rinsed and extracted normally, but without the
addition of surrogate compounds.
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The final pooled extract sample volume is recorded and an aliquot is used for the
TCO GC/FID, while duplicate aliquots are used in the GRAY measurements.
10
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Section 5
Total Chromatographic Organic (TCO) Method
The TCO Method has been described in detail in the Level 1 Procedures Manual3 and
revised as an interim EPA/AEERL operating procedure (Appendix C). The identified range of
organic compounds is defined by boiling point range, in this case 100-300°C. Compounds with
boiling points between 100°C and 300°C are analyzed by GC with an FID detector after
collection using a Method 0010 sampling train. The TCO procedure is carried out by analysis of
a dichloromethane extract (a combination of the extracts from the three major components of the
sampling train). The analysis is generally performed in the laboratory after extraction and
compositing of the extracts of the individual components of the Method 0010 sampling train.
TCO Method
The TCO Method, in its current form, is a capillary GC/FID method quantifying
chromatographable material in the 100°C to 300°C boiling point range. An aliquot of the
Method 0010 dichloromethane extract is injected onto a capillary GC column with an FID
detector, and the peak areas are summed over the retention time window that encompasses the
TCO boiling point range. The entire analysis window is established by injecting w-heptane (C7)
and w-heptadecane (C17) as the reference peaks between which the TCO integration will occur.
As described in the method, heptane and heptadecane are used as retention time reference peaks
for boiling point.
The TCO value is determined from the calibration standard curve, generated with
hydrocarbon standards which fall within the TCO range, specifically decane (C10), dodecane (C12),
and tetradecane (C14). An integrator or GC data system is used to record the data points as they
11
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are obtained from the injections of calibration standards and samples. The organics identified in
the prescribed boiling point range are quantified and summed (totalled) to obtain the TCO portion
of the total organics number. Reporting units are generally in terms of jig per sample, which is
then converted to |ig/m3, based on the sampling volume.
Analysis may be performed using a capillary (preferred) or packed column GC. A non-
polar or slightly polar column is used to provide adequate resolution and analysis in a total run
time of approximately 45 minutes. A 15 to 30 m non-polar wide bore column (0.32 mm) has been
found to be effective for TCO analysis. As a capillary or packed column procedure, the GC/FID
is operated in a manner consistent with the manufacturer's recommendations for gas flow,
temperature zones, and injection volume. Analysis is performed most easily using a GC with a
liquid autosampler, so that calibrations and sample injections can be performed in a consistent and
automated fashion. The GC used for TCO analysis is calibrated using specific hydrocarbon
standards. A multipoint calibration of at least three different concentrations in duplicate is
required for this procedure. After calibration has been performed, a daily quality control (QC)
check sample is run to verify that the GC is performing correctly. The QC check sample is run
with a standard in the middle of the working range of the GC calibration standards.
While it is understood that the compounds in this volatility and boiling point range might
include compounds that are not hydrocarbons, the FID detector is seen as a good all-purpose
detector for the quantification of the sample extracts.
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Section 6
Gravimetric (GRAV) Method
The third component of the total organics measurement process is called gravimetric mass
(GRAV). The GRAV Method has also been described in detail in the Level 1 Procedures
Manual3 and also revised as an interim EPA/AEERL operating procedure (Appendix D). The
GRAV procedure is carried out by analysis of an aliquot of the same dichloromethane extract
from the Method 0010 sampling train as was used for TCO determinations. GRAV is a
gravimetric mass measurement of the nonvolatile (boiling point >300°C) organics found in the
extract of the sampling train, which was established for the Level 1 procedures by an exhaustive
study of hydrocarbon evaporative properties. The range of organics is defined by boiling point, in
this case greater than 300°C. The analysis is generally performed in the laboratory after
extraction and compositing of the extracts of the individual components of the Method 0010
sampling train.
GRAV Method
The GRAV Method, in its current form, quantifies nonvolatile organic material with a
boiling point greater than 300°C. A carefully measured aliquot of the Method 0010
dichloromethane extract is placed in a precleaned aluminum weighing pan and allowed to dry in
air at room temperature, then come to complete dryness in a room temperature desiccator, while
exposure to dust and contaminants are minimized. The residue in the pan is weighed accurately,
and the mass is recorded to determine the GRAV value. For this procedure, the three individual
dichloromethane extracts from Method 0010 are pooled and reduced to a final volume of 5.0 mL.
A volume of 1 mL of the pooled extract is used for the GRAV determinations, which are
performed in duplicate. Other final extract and GRAV aliquot volumes may be used, but the
sample extraction and concentration procedures of Method 3542 (Appendix G) should be
13
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followed closely to avoid loss of more volatile organics. The GRAY organics in the greater than
300°C range are measured on an analytical balance and recorded for the GRAY portion of the
total organics number. This value, in jig, is converted to units of jig per sample, which is then
divided by sample volume to obtain |ig/m3. This sum is added to the previously determined TCO
and field GC values to find the total organics value, in units of micrograms per m3.
14
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Section 7
References
1. Revised Draft of Risk Assessment Implementation Guidance for Hazardous Waste
Combustion Facilities. Memorandum from Michael H. Shapiro, Office of Solid Waste. U.
S. Environmental Protection Agency, May 5, 1994.
2. Johnson, Larry D., M. Rodney Midgett, Ruby H. James, Michael M. Thomason, and M.
LisaManier. Screening Approach for Principal Organic Hazardous Constituents and
Products of Incomplete Combustion. Journal of Air & Waste Management Association.
Vol. 39, No. 5, May 1989.
IERL-RTP Procedures Manual: Level 1 Environmental Assessment (Second Edition). U.S.
Environmental Protection Agency. EPA-600/7-78-201. October 1978.
15
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Appendix A
Recommended Operating Procedure for
Field Gas Chromatography
(From SW-846, Method 8240 and
Method 18 - 40 CFR Part 60, Appendix A)
16
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RECOMMENDED OPERATING PROCEDURE FOR
FIELD GAS CHROMATOGRAPHY
A.1.0 INTRODUCTION
Field analyses are performed for samples that are subject to significant degradation if
analysis is delayed even for the amount of time required to ship samples to a laboratory, or in
situations where performing analysis in the field is preferable to handling and shipping samples
such as Tedlar® bags. In determining Total Organics, field gas chromatography is performed to
determine compounds in the Cl - C7 hydrocarbon range. This range encompasses alkanes,
alkenes, cyclic compounds, and functionalized organic compounds. For example, methane,
chloromethane, formaldehyde, and methanol are all Cx compounds. The methodology is
applicable to Cl - C7 hydrocarbons, organic compounds boiling in the range -160°C to 100°C.
When performing field gas chromatographic analysis, species eluting in the specified boiling point
range are quantified as n-alkanes. The sensitivity of the flame ionization detector varies from
compound to compound, but n-alkanes as a class have a higher flame ionization response than
other classes of compounds such as oxygenated or halogenated hydrocarbons. Therefore, using
n-alkanes as calibrants and assuming equivalent responses for all other compounds in the
appropriate boiling point range tends to bias results low. That is, if an alkane standard and a non-
alkane peak have equivalent system responses, the non-alkane peak is assigned a quantitative
value equivalent to the alkane. The non-alkane peak, however, has a poorer response to the flame
ionization detector than the alkane. The amount of non-alkane required to produce the same
response as an alkane may be several times higher than the amount of alkane, so the reported
value shows a low bias.
A.2.0 SCOPE AND APPLICATION
This procedure defines the field gas chromatographic analysis of gaseous stationary source
emissions sampled into a Tedlar® bag for Cl - C7 hydrocarbons, a chromatographic elution range
defining organic compounds boiling in the range of -160°C to 100°C.
A-l
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A.3.0 SUMMARY OF METHOD
A gas sample contained in a Tedlar® bag is analyzed in the field by gas
chromatography/flame ionization detection (GC/FID). The instrument is set up in the field with
column and conditions appropriate for the analysis of Cx - C7 n-alkanes. Retention times are
determined and calibration is performed with a certified gaseous standard of Cl - C7 alkanes in air
or nitrogen. Compounds of interest are identified by retention times or retention time ranges and
quantitative analysis is performed.
A.4.0 SAMPLE HANDLING AND PRESERVATION
Samples for this analysis are contained in Tedlar® bags. These samples should be
analyzed as soon after acquisition as possible, preferably within two hours. Exposure to extremes
of light and temperature should be avoided.
A.5.0 APPARATUS AND REAGENTS
A.5.1 Gas Chromatograph
The gas chromatograph to be used for this analysis must be capable of being moved into
the field, with a flame ionization detector, temperature-controlled sample loops of varying sizes
with a valve assembly, temperature-programmable oven, and an appropriate chromatographic
column to obtain the resolution desired for the analysis.
A.5.2 Recorder/Integrator/Data System
A recorder is required. Appropriate parameters are 1 inch/min chart speed, 1 mV full
scale, 1 sec full scale response time. An integrator is required. The function of both the recorder
and integrator may be superseded by a data system, if available. Parameters which should be
specified and recorded in the instrument log include noise suppression, up-slope sensitivity, down-
A-2
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slope sensitivity, baseline reset delay, area threshold, front shoulder control, rear shoulder control,
and data sampling frequency.
A.5.3 Columns
For the Cx -C4 hydrocarbons, a packed stainless steel SP-1000® column (6 ft x 1/8 inch
outer diameter), or equivalent which can be calibrated over the specified hydrocarbon range is
required. Some possible equivalent columns include PLOT® or TCEP® columns. If a PLOT
column is used, this column could be used for the C5 to C7 hydrocarbon range as well. An
alternative is to use a second gas chromatograph with a generic nonpolar packed or capillary
column for the C5 to C7 range and a flame ionization detector.
A.5.4 Gas Standard
A certified n-alkane gas standard of Cl - C7 n-alkanes in air or nitrogen is required. The
concentrations of the alkanes in the certified standard may range from 5-100 ppm. A multipoint
calibration curve at different concentrations may be obtained by using sample loops of different
sizes or multiple gas cylinders at different concentrations.
A.5.5 Cylinder Gases
Helium carrier gas, hydrocarbon free, as recommended by the manufacturer for operation
of the detector and compatibility with the column is required. Fuel (hydrogen), as recommended
by the manufacturer for operation of the flame ionization detector, and zero air, hydrocarbon free
air for operation of the flame ionization detector, are required.
A-3
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A.5.6 Regulators
Appropriate regulators are required for all gas cylinders for both support gases and for
certified gaseous standards.
A.5.7 Teflon® Tubing
Diameter and length determined by requirements for connection of gas cylinder regulators
and the gas chromatograph.
A.6.0 GAS CHROMATOGRAPH SETUP AND CHECK
The gas chromatograph must be completely calibrated at each new test site in the field.
Whenever the gas chromatograph is set up, the following parameters must be verified for correct
operation:
1) All support gas supplies must be at the proper pressure.
2) Verify that the carrier gas flow to the analytical column is correct (for a packed
column, the gas flow rate should be 30 ± 2 mL/min; for a capillary column, flow
rate will depend upon the column diameter and should be adjusted according to the
manufacturer's specifications for the column). Flow rate is checked at the
analytical column outlet after disconnection from the detector. The instrument
must be at ambient temperature.
3) Verify that the hydrogen flow is appropriate for the operation of the flame
ionization detector. The flow rate is checked at the control panel on the gas
chromatograph.
4) Verify that the air flow is appropriate for the operation of the flame ionization
detector. The air flow rate is checked at the gas control panel on the gas
chromatograph.
5) Verify that the electrometer is functioning properly. The electrometer must be
balanced and the bucking controls set as required.
6) Verify that recorder/integrator/data system are functioning properly.
A.7.0 CALIBRATION
A-4
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To determine the temperature ranges for reporting the results of GC analyses for the Cx -
C7 compounds, the gas chromatograph is given a normal boiling point - retention time calibration.
The n-alkanes, their boiling points, and the data reporting ranges are shown below.
Compound
methane
ethane
propane
butane
pentane
hexane
heptane
Boiling Point,
°C
-161
-88
-42
0
36
69
98
Reporting Range,
°C
-160 to -100
-100 to -50
-50 to 0
Oto30
30 to 60
60 to 90
90 to 98
Report As
c,
c,
c,
c.
c,
c«
C7
To perform a multipoint calibration, connect the Cx - C7 certified standard gas cylinder to
the sampling valve, and allow the gas to flow through the valve at a constant, low, and
reproducible flow rate of 20 mL/min measured at the sample valve outlet using a bubble
flowmeter. When the sample valve has purged (approximately 5 min), allow the sample loop
pressure to equilibrate to atmospheric pressure and actuate the valve and inject the contents of the
sample loop into the gas chromatograph. Simultaneously, start the integrator and/or data system
and the temperature programmer, if used. Obtain chromatograms and integrator/data system
output. Retention times and responses shall agree to within 5% relative standard deviation.
Repeat the standard injection until two consecutive injections give area counts within 5 percent of
their mean value. The average value multiplied by the attenuation factor is then the calibration
area value for the concentration.
A-5
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The multipoint calibration must encompass at least three concentration levels, with each
point analyzed at least in duplicate (a minimum of six calibration data points for each n-alkane).
The different concentrations are achieved either by analysis of standards from cylinders at three
different concentrations or by use of sample loops of different sizes with one certified gaseous
standard. Prepare a plot of the concentration versus the calibration area values, perform a
regression analysis, and draw the least squares line.
A.8.0 DAILY CALIBRATION CHECK
The Cj - C7 certified standard gas mixture will be injected and analyzed at the start of each
day, at a concentration at approximately the midpoint of the calibration curve. Retention times
and responses for each component should agree with the initial calibration data to within ±10
percent. If the daily calibration check meets this specification, the full calibration need not be
repeated.
A.9.0 ANALYSIS OF SAMPLES
If any doubt exists concerning the relationship between the stationary source sample GC
peaks and the GC peaks obtained from calibration, a small amount of the calibration gas should be
spiked with the sample in order to verify retention times.
To perform the analysis of gaseous samples, the chromatograph, recorder, integrator/data
system must be set up according to the manufacturer's manuals and calibrated. Operating
parameters should be confirmed. The operating parameters are to be listed on each
chromatogram, and each recorder chart should be labeled. The sample bag should be connected
to the gas sample valve, the sample loop purged with the sample, and the contents of the loop
should be injected. The integrator/data system and recorder should be started simultaneously with
injection.
A-6
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If any doubt exists concerning the relationship between the stationary source sample GC
peaks and the peaks obtained from analysis of the calibration standard, a small aliquot of the
calibration gas should be spiked with the sample in order to verify retention times.
A.10.0 CALCULATIONS FOR Ct - C7 HYDROCARBONS
The calibration curve for the n-alkanes is constructed in the following manner:
1) For each alkane, the average retention time and relative standard deviation are
calculated.
2) Plot boiling point of each alkane versus the average retention times (in seconds).
3) Draw the curve, manually or by computer.
4) On the curve, locate and record the retention times corresponding to the reporting
ranges: -160°C to -100°C, -100°C to -50°C, -50°C to 0°C, 0°C - 30°C, 30°C
to 60°C, 60°C to 90°C, and 90°C to 98°C.
5) Calculate average area response and relative standard deviations for the propane
calibration standard.
6) Plot response (|iV/sec) as ordinate versus concentration of the standard in mg/m3
injected as abscissa. Draw in the curve. Perform least squares linear regression
and obtain the slope (jiV/sec * m3/mg).
7) In each retention time range of the sample, sum up the peak areas.
8) Convert peak areas (jiV / sec) to mg/m3 by dividing by the proper response (slope
factor).
9) Record the total concentration of material in each retention time range.
A-7
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Appendix B
Recommended Operating Procedure for
Purge and Trap Gas Chromatography
With FID Detection
(From SW-846 Method 8240 and Draft Method 0040)
A-8
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RECOMMENDED OPERATING PROCEDURE FOR
PURGE AND TRAP GAS CHROMATOGRAPHY
WITH FID DETECTION
B.1.0 INTRODUCTION
As a complement to the Field Gas Chromatography analysis of total organics, the
condenser component of the Draft Method 0040 sampling train is analyzed using purge and trap
techniques and an FID detector. In determining total organics, purge and trap gas
chromatography is performed to determine compounds in the Cx - C7 hydrocarbon range. This
range encompasses alkanes, alkenes, cyclic compounds, and functionalized organic compounds.
For example, methane, chloromethane, formaldehyde, and methanol are all Cl compounds. The
methodology is applicable to Cl - C7 hydrocarbons, organic compounds boiling in the range -
160°C to 100°C. In performing purge and trap gas chromatographic analysis, species eluting in
the specified boiling point range are quantified as n-alkanes. The sensitivity of the flame
ionization detector varies from compound to compound, but n-alkanes as a class have a higher
flame ionization response than other classes of compounds such as oxygenated or halogenated
hydrocarbons.
B.2.0 SCOPE AND APPLICATION
The field gas chromatographic analysis encompasses gaseous stationary source emissions
sampled into a Tedlar® bag in the sampling train. Analysis is performed for the organic
compounds boiling in the range of-160°C to 100°C. In Draft Method 0040, the condenser, the
condensate trap and the sample line from trap to the Tedlar® bag are carefully rinsed and the
combined water sample is transferred to a graduated cylinder. After carefully measuring the
sample volume, the water sample is transferred to a 20 mL or 40 mL amber glass VOA vial with a
Teflon® septum screw cap with zero void volume. VOA vials under zero headspace conditions
may be stored on ice or in a refrigerated container until analysis. This procedure defines the gas
chromatographic analysis of gaseous stationary source emissions sampled into the condensate
component of a Draft Method 0040 train.
B-l
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B.3.0 SUMMARY OF METHOD
The volatile compounds are introduced into the gas chromatograph (GC) by the purge and
trap method. The components are separated via the GC and detected using a flame ionization
detector (FID), which is used to provide quantitative information.
An inert gas is bubbled through the solution at ambient temperature and the volatile
components are efficiently transferred from the aqueous phase to the vapor phase. The vapor is
swept through a sorbent column where the volatile components are trapped. The sorbent
columns of choice are a VOCOL® or VOCARB 3000® design, or equivalent. After purging is
completed, the sorbent column is heated and backflushed with inert gas to desorb the components
onto a GC column. The GC column is heated via a temperature program to elute the
components, which are detected with an FID detector.
A volatile organic sample contained in a VOA vial is analyzed in the laboratory by gas
chromatography/flame ionization detection (GC/FID). The instrument is set up with column and
conditions appropriate for the analysis of C4 - C7 n-alkanes. Retention times are determined and
calibration is performed with a liquid standard of C5 - C7 alkanes. Compounds of interest are
identified by retention times or retention time ranges and quantitative analysis is performed.
B.4.0 SAMPLE HANDLING AND PRESERVATION
Samples for this analysis are transferred from the condenser vessel to VOA vials. These
samples should be analyzed as soon after acquisition as possible, preferably within two weeks of
collection. Samples are refrigerated without headspace in the vials until analysis. Exposure to
extremes of light and temperature should be avoided.
B-2
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B.5.0 APPARATUS AND REAGENTS
Apparatus and reagents needed to perform the purge and trap analysis techniques are
summarized in the following paragraphs. Glassware, vials, laboratory refrigerators, compressed
gas storage, and items customarily found in an analytical laboratory are assumed to be readily
available.
B.5.1 Purge and trap device
The purge and trap device consists of three major components: a purge chamber for the
water, a trap, and a desorber capable of rapidly heating the trap. The purge chamber should be
designed to accept 5 mL samples of water with a water column of at least 3 cm. The purge gas
must pass through the water column as finely divided bubbles, normally obtained by passing the
gas through a medium porosity glass frit. The packing material for the trap should be a
commercially available sorbent material (or combination of materials) capable of trapping and
releasing low boiling (volatile) organic compounds. VOCOL® or VOCARB 3000® (Carbopack
B and Carboxen® in series) sorbent packing materials, or an equivalent sorbent, are acceptable
for the traps, providing they adequately trap and desorb the organic components of interest. The
desorber should be capable of rapidly heating the trap to a temperature of at least 180°C for
desorption.
B.5.2 Reagent water
Reagent water for this analysis is defined as water in which interferents are not observed at
the method detection limit (MDL) of the parameters of interest. Purified water (carbon filtration
or deionized distilled water) may be used. Alternatively, water may be boiled and subjected to a
bubbled stream of inert gas, then sealed until used.
B-3
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B.5.3 Gas Chromatograph Setup
For the Cl -C4 hydrocarbons, a packed stainless steel SP-1000® column (6 ft x 1/8 inch
outer diameter), or equivalent which can be calibrated over the specified boiling point range is
required. Some possible equivalent columns include PLOT® or TCEP® columns. If a PLOT
column is used, this column could be used for the C5 to C7 hydrocarbon range as well. An
alternative is to use a second gas chromatograph with a generic nonpolar packed or capillary
column for the C5 to C7 range and a flame ionization detector.
The gas chromatograph must be completely calibrated for use. Whenever the gas
chromatograph is set up, the following parameters must be verified for correct operation:
1) All support gas supplies must be at the proper pressure.
2) Verify that the carrier gas flow to the analytical column is correct (for a packed
column, the gas flow rate should be 30 ± 2 mL/min; for a capillary column, flow
rate will depend upon the column diameter and should be adjusted according to the
manufacturer's specifications for the column). Flow rate is checked at the
analytical column outlet after disconnection from the detector. The instrument
must be at ambient temperature.
3) Verify that the hydrogen flow is appropriate for the operation of the flame
ionization detector. The flow rate is checked at the control panel on the gas
chromatograph.
4) Verify that the air flow is appropriate for the operation of the flame ionization
detector. The air flow rate is checked at the gas control panel on the gas
chromatograph.
5) Verify that the electrometer is functioning properly. The electrometer must be
balanced and the bucking controls set as required.
6) Verify that recorder/integrator/data system are functioning properly.
B.5.4 Regulators
Appropriate regulators are required for all gas cylinders for detector and carrier gases.
B-4
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B.5.5 Liquid Standard
A set of n-alkane liquid standards of C5 - C7 n-alkanes is required. The concentrations of
the alkanes in the standard may range over several orders of magnitude within the working range
of the GC/FID. A multipoint calibration curve at different concentrations may be obtained by
using multiple dilutions of a stock standard solution.
Calibration standards should be prepared from secondary dilution of stock standards. The
solutions should be prepared in methanol, with one of the concentrations at a level near, but
above, the method detection limit. The remaining concentrations should correspond to the
expected range of concentrations found in real samples (not exceeding the working range of the
GC/FID system). Each standard should contain the straight chain hydrocarbons C5 to C7. The
lower boiling organic compounds (Cl to C3) are not expected to be found in the condensate
solutions collected in a Draft Method 0040 sampling train. If compounds are found with retention
times prior to the C4 retention time, an appropriate response factor will be used to determine the
concentration of those components and their value reported as C4 (butane) with the other organic
results.
B.5.6 Cylinder Gases
Helium carrier gas, hydrocarbon free, as recommended by the manufacturer for operation
of the detector and compatibility with the column. Fuel (hydrogen), as recommended by the
manufacturer for operation of the flame ionization detector, and zero air, hydrocarbon free air for
operation of the flame ionization detector, are required.
B-5
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B.5.7
Recorder/Integrator/Data System
A recorder is required. Appropriate parameters are 1 inch/min chart speed, 1 mV full
scale, 1 sec full scale response time. An integrator is required. The function of both the recorder
and integrator may be superseded by a data system, if available. Parameters which should be
specified and recorded in the instrument log include noise suppression, up-slope sensitivity, down-
slope sensitivity, baseline reset delay, area threshold, front shoulder control, rear shoulder control,
and data sampling frequency.
B.6.0 CALIBRATION
To determine the temperature ranges for reporting the results of GC analyses for the C5 -
C7 compounds, the gas chromatograph is given a normal boiling point - retention time calibration.
The n-alkanes, their boiling points, and the data reporting ranges are shown below.
Compound
methane
ethane
propane
butane
pentane
hexane
heptane
Boiling Point,
°C
-161
-88
-42
0
36
69
98
Reporting Range,
°C
-160 to -100
-100 to -50
-50 to 0
Oto30
30 to 60
60 to 90
90 to 100
Report As
c,
c,
c,
c.
c,
cfi
C7
To perform a multipoint calibration for purge and trap analysis, the most practical method
is to prepare liquid standards in methanol of the C5 through C7 alkanes by dilution of a primary
stock. A set of dilutions is prepared, covering the working range of the instrument and the
solutions are spiked directly into clean reagent water in VOA vials. The purge and trap system is
activated to purge the standard from the purge vessel into the trap. After trapping is complete,
the desorber is activated (heated) and simultaneously the integrator and/or data system and the
B-6
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temperature programmer are started. Obtain chromatograms and integrator/data system output.
Retention times and responses shall agree to within 5% relative standard deviation. Repeat the
standard injection until two consecutive injections give area counts within 5 percent of their mean
value. The average value multiplied by the attenuation factor is then the calibration area value for
the concentration.
The multipoint calibration must encompass at least three concentration levels, with each
point analyzed at least in duplicate (a minimum of six calibration data points for each n-alkane).
The different concentrations are achieved by analysis of standards at three different concentrations
of liquid standards of the C5 through C7 alkanes. Prepare a plot of the concentration versus the
calibration area values, perform a regression analysis, and draw the least squares line.
B.7.0 DAILY CALIBRATION CHECK
A C5 - C7 standard mixture will be injected (purge and trap) and analyzed at the start of
each day, at a concentration at approximately the midpoint of the calibration curve. Retention
times and responses for each component should agree with the initial calibration data to within ±
10 percent. If the daily calibration check meets this specification, the full calibration need not be
repeated.
B.8.0 ANALYSIS OF SAMPLES
If any doubt exists concerning the relationship between the stationary source sample GC
peaks and the GC peaks obtained from calibration, a small amount of the calibration standard
should be spiked with the sample in order to verify retention times.
To perform the analysis of condensate water samples, the chromatograph, recorder,
integrator/data system must be set up according to the manufacturer's manuals and calibrated.
Operating parameters should be confirmed. The operating parameters are to be listed on each
chromatogram, and each recorder chart should be labeled. The sample vial should be correctly
B-7
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labeled and transferred to the purge vessel. After purging and trapping, the organics are desorbed
onto the head of the GC column ("injection"). The integrator/data system and recorder should be
started simultaneously with injection.
B.10.0 CALCULATIONS FOR C5 - C7 HYDROCARBONS
The calibration curve for the n-alkanes is constructed in the following manner:
1) For the alkanes C5 through C7, the average retention time and relative standard
deviation are calculated.
2) Plot boiling point of each alkane versus the average retention times (in seconds).
3) Draw the curve, manually or by computer.
4) On the curve, locate and record the retention times corresponding to the reporting
ranges: 0°C - 30°C, 30°C to 60°C, 60°C to 90°C, and 90°C to 100°C .
5) Calculate average area response and relative standard deviations for the hexane
calibration standard.
6) Plot response (|iV/sec) as ordinate versus concentration of the standard in mg/m3
injected as abscissa. Draw in the curve. Perform least squares linear regression
and obtain the slope (jiV/sec * m3/mg).
7) In each retention time range of the sample, sum up the peak areas.
8) Convert peak areas (jiV / sec) to mg/m3 by dividing by the proper response (slope
factor).
9) Record the total concentration of material in each retention time range.
B-8
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Appendix C
Recommended Operating Procedure for Total
Chromatographable Organics (TCO) Analysis
(This document was originally prepared for the EPA/AEERL Laboratory in RTF, NC and
developed and reviewed by the QA Program of AEERL, under the direction of Judith S. Ford,
QA Manager of EPA/AEERL)
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TABLE OF CONTENTS
Section Page
C.I INTRODUCTION 1
C.I.I Scope 1
C.I.2 Limitations 1
C.I.3 Definitions 2
C.2 STARTUP 3
C.2.1 Personnel Requirements 3
C.2.2 Facilities Requirements 3
C.2.3 Safety Requirements 3
C.2.4 Apparatus 4
C.2.4.1 Equipment Needed 4
C.2.4.2 Reagents and Materials 4
C.2.4.3 Maintenance 4
C.2.4.4 Theory Of FID Detector 5
C.2.5 Interferences 5
C.3 OPERATION 6
C.3.1 Summary of Method 6
C.3.2 Samples/Sampling Procedures 6
C.3.3 Operation 8
C.3.4 Analysis 9
C.4 TROUBLESHOOTING 10
C.4.1 Calibration 10
C.4.2 Method Precision and Accuracy 11
C.5 DATA REDUCTION 12
C.5.1 Calculations 12
C.5.2 Data Reporting 12
C.6 QUALITY ASSURANCE/QUALITY CONTROL 13
C.6.1 QC Checks 13
C.6.2 QC Controls 13
C.7 REFERENCES 14
-------
LIST OF TABLES
Page
C.I Instrumental Operating Conditions for Gas Chromatography 7
-------
Disclaimer
This recommended operating procedure has been prepared for the sole use of the Air and
Energy Engineering Research Laboratory, U.S. Environmental Protection Agency, Research
Triangle Park, North Carolina, and may not be specifically applicable to the activities of other
organizations.
Acknowledgements
Assisting in the preparation of this procedure, dated 10/88 as Document No. AEERL/13,
were Robert F. Martz, Acurex Corporation, Research Triangle Park, NC, under EPA Contract
68-02-4701 for on-site technical support to AEERL; and Joseph D. Evans and Anne E. Worth,
Research Triangle Institute, Research Triangle Park, NC, under EPA Contract 68-02-4291 for
Quality Assurance (QA) support to AEERL. Judith S. Ford, QA Manager for AEERL, is the
Project Officer for the QA contract with Research Triangle Institute.
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SECTION C.I
INTRODUCTION
C.1.1 Scope
This method provides semi-quantitative data for organic compounds with boiling points
between 100 and 300°C. Samples that might include organic compounds in this volatility range
are organic liquids, solid sample extracts, aqueous extracts, extracts from Source Assessment
Sampling System (SASS) and Modified Method 5 (MM5) train sorbent modules, and liquid
chromatography (LC) fractions obtained from those samples. This method is based on separating
the components of a gas or liquid mixture in a gas chromatography (GC) column and measuring
the separated components with a suitable detector.
This upper end of applicability is limited by column overloading and detector saturation.
Typical range is 1 to 20 mg/mL. The operating range can be extended by dilution of samples with
solvent (e.g., dichloromethane). The sensitivity limit shall be determined by the minimum
detectable concentration of standards.
C.1.2 Limitations
Recommended operating procedures (ROPs) describe non-routine or experimental
research operations where some judgment in application may be warranted. ROPs may not be
applicable to activities conducted by other research groups and should not be used in place of
standard operating procedures. Use of ROPs must be accompanied by an understanding of their
purpose and scope. Questions should be directed to AEERL or to project personnel listed in the
Acknowledgments.
C-l
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C.1.3 Definitions
Accuracy - The degree of agreement between an observed value and an accepted
reference value. Accuracy includes a combination of random and systematic error
or bias components which are due to sampling and analytical operations; a data
quality indicator.
Calibrate - To determine, by measurement or comparison with another standard,
the correct value of each scale reading on a meter or other device, or the correct
value for each setting of a control knob. The levels of calibration standards should
bracket the range of planned measurements.
Calibration Standard - A substance or reference material used to calibrate the
instrument.
Method Blank - A clean sample processed simultaneously with samples
containing an analyte of interest through all steps of the analytical procedure.
Precision - The degree of variation among individual measurements of the same
property, usually obtained under similar conditions; a data quality indicator.
Precision is usually expressed as standard deviation, variance or range, in either
absolute or relative terms.
Quality Control (QC) Sample - A sample prepared from substances or materials
of known composition and quantity. It is used to assess the performance of a
measurement method or portions thereof. It is intended primarily for routine
intralaboratory use in controlling precision and bias in the method. It should be
prepared from, or be traceable to, a standard other than the calibration standard.
Reagent Blank - A sample of reagent(s), without the target analyte, introduced
into the analytical procedure at the appropriate point and carried through all
subsequent steps to determine their contribution to error in the observed value.
C-2
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SECTION C.2
STARTUP
C.2.1 Personnel Requirements
This ROP is written for individuals with a BS/BA degree in chemistry and at least two
years experience in gas chromatography, or equivalent.
C.2.2 Facilities Requirements
This procedure requires a standard analytical chemistry laboratory with counter space,
secured areas for compressed gas storage, and electricity to operate the equipment. Flasks,
beakers, tubing, etc., customarily found in such a laboratory are also needed and assumed to be
readily available. GC tools (e.g., wrenches, screwdrivers, and spare parts, etc.) also need to be
available in the laboratory.
C.2.3 Safety Requirements
Routine safety precautions required in any analytical chemistry laboratory are applicable
here. These include such measures as no smoking while in the laboratory; wearing safety glasses,
lab coats, and gloves when handling samples; and handling organic solvents in a fume hood, etc.
Compressed gases considered to be fuels (e.g., hydrogen) must be stored on a pad outside the
confines of the laboratory. A safety shower, eye wash, first aid kit, and fire extinguisher must be
readily available inside the laboratory.
C-3
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C.2.4 Apparatus
C.2.4.1 Equipment Needed
• Gas chromatography: With packed column and/or capillary column capabilities,
oven temperature controller, and flame ionization detector (FID) (e.g., Perkin
Elmer Sigma 115 or Hewlett Packard 5890).
• Autosampler (optional): Capable of handling methylene chloride extracts and
appropriate wash vials.
• Autosampler vials (optional): Clear glass with Teflon® faced crimp caps,
typically 100 jiL or 1 mL size.
• Crimping tool (optional): Used to secure caps on autosampler vials.
C.2.4.2 Reagents And Materials
• Methylene chloride: Burdick and Jackson or equivalent grade.
• Syringe: 5 jiL or 10 jiL, gas tight, for hand injections. Otherwise, 3 jiL or 10 jiL
syringes are used for autosampler injections.
• Pasteur pipettes: Disposable, used for sample transfer.
• Pipette bulbs: 1 mL, amber
• Squeeze bottle: Teflon®, 250 mL or equivalent, used for methylene chloride
rinse of vials.
C.2.4.3 Maintenance
Glassware: Clean all glassware used in the total chromatographable organics
(TCO) analysis by the method described in Reference 1.
Gas Chromatograph: Change the GC inlet septum daily; follow this with a
column bakeout at 250°C for 20 minutes or, until the detector response is stable
and all evidence of contamination is gone (no peaks), or run an injection of clean
solvent to verify column contamination is eliminated. Repeat this procedure
during the run if evidence of septum failure appears (e.g., increasing peak elution
time with each run, or major loss of sensitivity).
C-4
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C.2.4.4 Theory Of FID Detector
Flame ionization detectors operate by burning organic compounds in the detector's flame.
The burning process oxidizes the carbon atoms, producing electrons and positive ions. An anode
and cathode on either side of the flame collect the charged particles, and the resulting current is
proportional to the concentration of oxidized carbon in the sample. Instrument electronics
convert the detector current to a voltage, which changes linearly with changes in analyte
concentration.
C.2.5 Interferences
The analytical system shall be demonstrated to be free from internal contaminants on a
daily basis by running a bakeout or a QC sample. A reagent blank must be run for each new batch
of reagents used to determine that reagents are contaminant-free. This is verified by an
instrument response less than the detection limit.
If duplicate runs of a sample show increasing concentration greater than 15% or if cross-
contamination is suspected (e.g., high-level sample followed by a low-level sample), a reagent
blank shall be run to verify no contamination in the system. If contamination is evident, the
column shall be baked out at approximately 250°C for twenty minutes or until the detector is
stable, and the blank check repeated.
C-5
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SECTION C.3
OPERATION
C.3.1 Summary of Method
TCO analysis quantifies chromatographable material with boiling points in the range of
100° to 300°C. This analysis is applied to all samples that might contain compounds in this
volatility and boiling point range.
For TCO analysis, a 0.9 to 3 L portion of the extract is analyzed by gas chromatography
using a flame ionization detector (FID). Column conditions are described in this document in
tabular form in Table 3-1. The peak areas are converted to concentration values using
quantitative calibration standards.
For more information, consult Lentzen et al., IERL Procedures Manual: Level 1
(Reference 1).
C.3.2 Samples/Sampling Procedures
Samples for TCO analysis arrive or are prepared as methylene chloride (or occasionally as
methanol) extracts of environmental samples, filters, resins, or ambient sampling components. An
aliquot of the extract is transferred to a TCO vial and loaded into the autosampler as required.
All samples will be stored in a refrigerator at or below 4°C to retard analyte degradation.
Samples will be analyzed as soon as possible after sample receipt and preparation to avoid loss of
sample due to volatilization and degradation.
C-6
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TABLE C-l
INSTRUMENTAL OPERATING CONDITIONS FOR
GAS CHROMATOGRAPHY
Column
Fused Silica Capillary Column
(15 meters, wide bore, typically
DB-1, DB-5, or equivalent)
Packed Column (Methyl
Silicone oil or equivalent,
1/8 in. x 6 ft. steel)
Temperature
Program
40°C for 3 min, 8°C/min
increase to 250°C and hold for
total run time of 45 min
50°C for 5 min, 20°C/
min increase to 250°C,
then hold
Injector
300°C
300°C
Detector
F.I.D. at 300°C
F.I.D. at 300°C
Carrier Gas
Helium, 1-3 mL/min
Helium, 30 mL/min
Split Injector
(optional)
10/1 split ratio
Not Applicable
Injector Volume
Not to exceed 3 L (Typically 1
L)
1-5 L
Solvent
Dichloromethane (pesticide
grade, distilled in glass or
equivalent)
Dichloromethane
(pesticide grade, distilled
in glass or equivalent)
C-7
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C.3.3 Operation
Note: All glassware coming in contact with a sample shall be cleaned by
Level 1 procedures (Ref. 1). Briefly, this entails sequential cleaning with
soapy water, deionized water, 50:50 (V/V) nitric acid/sulfuric acid, deionized
water, methyl alcohol, and methylene chloride, followed by oven drying.
Those steps that are only applicable to automatic injection are shown with an
asterisk (*).
• Start up by the manufacturer's suggested method.
* • Replace septum on auto-sampler and column.
* • Ensure injection needle is in line with injection port. The autosampler
needle should be manually "injected" through the injection port to
verify alignment.
• Bakeout GC at 200 °C for 20 minutes until FID response is stable and
all evidence of column contamination is gone (no peaks), or run an
injection of clean solvent as the first injection of the day to verify that
column contamination is eliminated.
* • Load auto-sampler tray with samples.
* • Check the autosampler flush by placing the autosampler in manual
mode and flushing a vial of clean solvent through the needle assembly.
* • Set auto-sampler to inject approximately 1 L of samples. Capillary
column can be damaged if too great a volume is injected.
• Run a QC standard using the specified conditions to verify that the
system is operating properly. Check the TCO window (C7 to C17) to
ensure the range has not changed. (Retention times may change with
column aging.) The TCO window for calculations should be adjusted
as required.
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• Flush needle with solvent (dichloromethane) between injections.
• Run samples and collect data.
• Analyze data according to the method described in Section 3.4.
• After all analyses are complete, bakeout the column at 200 °C for
20 minutes, or run clean solvent as a "sample."
• Shut down instrument by method suggested by manufacturer.
C.3.4 Analysis
The peak area (FID response/ L) is summed over the TCO range window
and corresponding TCO value (mg/mL) is determined from the calibration curve, hi
the event that the TCO value is outside the linear working range, the sample shall be
concentrated or diluted, depending on the requirements, and reanalyzed. If there is
not enough sample to concentrate, the values are reported as found, and an
appropriate qualifying statement is included in the analytical report.
It is important that the observed values of the total integrated area for samples
be corrected by subtracting an appropriate solvent blank, prepared in the same
manner as the samples.
C-9
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SECTION C.4
TROUBLESHOOTING
C.4.1 Calibration
Quantitative calibration of the TCO procedure is accomplished by the use of
mixtures of known concentration of the normal hydrocarbons decane, dodecane, and
tetradecane. Retention time limits correspond to the TCO range of boiling points
and are defined by the peak maxima for n-heptane (C7, B.P. 98°C) and n-
heptadecane (C17, B.P. 303 °C). Therefore, integration of detector response should
begin at the retention time of C7 and terminate at the retention time of C17. The C7
and C17 peaks are not included in this integration. By this procedure, the integrated
area will cover material in the boiling range of approximately 100°C to 300 °C.
Calibrate the GC with dilutions of a stock solution, generating a
response/concentration curve. The calibration curve must be 1 and must have a
correlation coefficient greater than 0.97 to be acceptable. The preparation and
dilution of the stock solution is described below:
Weigh approximately 100 L aliquots of each (heptane, decane,
dodecane, tetradecane, and heptadecane, C7, C10, C12, C14, C17) (99% +
pure) into a 10 mL volumetric flask or septum-sealed vial. Weigh each
hydrocarbon successively into the vial starting from least volatile to
most volatile.
Dilute the vial contents up to approximately 3 mL with
dichloromethane.
Transfer this quantitatively to a clean, 10 mL amber volumetric flask
and add dichloromethane up to the 10 mL mark. This stock solution
will have approximately 22 mg (C7 to C12)/mL and
C-10
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15 mg(C14 to C17)/mL. Several (at least three) dilutions of the stock
solution are made to cover the linear working range.
C.4.2 Method Precision and Accuracy
Duplicate results by the same operator will be rejected if they differ by more
than 15%. The result of a quality control sample, run daily, will be considered
deficient if it differs by more than 15% from the preparation value. If this value falls
outside the accepted range, the system must be evaluated for the probable cause,
and a second standard run or a new calibration performed over the range of interest.
C-ll
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SECTION C.5
DATA REDUCTION
C.5.1 Calculations
The peak area (FID response/ L) is summed over the TCO window and a
corresponding TCO value (mg/mL) is determined from the calibration curve.
• Construct the calibration line by fitting a linear regression equation to
the results of the analysis of the calibration standard solution. The
concentration of the standards must fall within the linear working range
of the instrument and bracket the concentration of the sample. Use the
C10 to C14 standards for calibration.
Standard Calibration Equation:
R, =(M) Q + (B) (1)
Where R; = FID Response (total C10 to C14 Peaks),
Q = Concentration mg/L (total of C10 to C14 standards),
M = Slope of line, and
B = Intercept of line.
• Calculate the TCO value for the sample (Cu, measured value) and
blank (CB, blank value) by summing the FID response over the TCO
retention time span and calculating the concentration from the
calibration equation.
It is important that the observed values of the total integrated area for
samples be corrected by subtracting an appropriate solvent blank
prepared in the same manner as the samples. The sample is corrected
for the blank:
Cu corrected = Cu measured - CB (2)
C-12
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C.5.2 Data Reporting
The results of each TCO analysis should be reported as one number (in
milligrams), corresponding to the quantity of material in the 100° C to 300° C boiling
range in the original sample collected. If more information is available (e.g., cubic
meters of gas sampled), the mg/sample value can then be easily converted to the
required reporting units.
C-13
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SECTION C.6
QUALITY ASSURANCE/QUALITY CONTROL
C.6.1 PC Checks
If evidence of septum failure appears (e.g., increasing peak elution time with
each run or major loss of sensitivity), perform a column bakeout at 250°C for
twenty minutes or until the FID response is stable and all evidence of contamination
is gone (no peaks), or run an injection of clean solvent to verify that column
contamination is eliminated.
C.6.2 PC Controls
Run a reagent sample for each new batch of reagent or lot of solvent used. If
the analysis fails to show organic contaminants to be below detection limits under
identical instrument operating conditions as used for samples, then the reagent shall
be distilled in glass and retested, or the reagent batch will be unacceptable for TCO
analyses.
Prepare a QC sample that is approximately mid-way in the linear working
range. Run this QC sample daily to verify the performance of the GC. Determine
the TCO value using the calibration curve and its value plotted compared to the
theoretical value. If two runs of the QC sample differ by more than 15% of the
actual value, prepare a new QC sample and repeat the test. If the new sample fails
the test, determine if there is a loose column connection, septum, or altered split
flow. After correction, run a new QC sample. If the new sample fails the test, re-
calibrate the instrument and/or perform a column change if needed.
C-14
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SECTION C.7
REFERENCES
1. Lentzen, D.E., D.E. Wagoner, E.D. Estes, and W.F. Gutknecht. IERL-RTP
Procedures Manual: Level 1 Environmental Assessment (Second Edition).
EPA 600/7-78/201, NTIS No. PB 293-795, pp. 140-142, October 1978.
C-15
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Appendix D
Recommended Operating Procedure for Gravimetric (GRAV)
Analysis of Organic Extracts
(This document was originally prepared for the EPA/AEERL Laboratory in RTF, NC and
developed and reviewed by the QA Program of AEERL, under the direction of Judith S. Ford,
QA Manager of EPA/AEERL)
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Disclaimer
This recommended operating procedure has been prepared for the sole use of the Air and
Energy Engineering Research Laboratory, U.S. Environmental Protection Agency, Research
Triangle Park, North Carolina, and may not be specifically applicable to the activities of other
organizations.
Acknowledgements
Assisting in the preparation of this procedure, dated 9/86 as Document No. AEERL/12,
were Robert F. Martz, Acurex Corporation, Research Triangle Park, NC, under EPA Contract
68-02-4701 for on-site technical support to AEERL; and Monica Nees, Research Triangle
Institute, Research Triangle Park, NC, under EPA Contract 68-02-4291 for Quality Assurance
(QA) support to AEERL. Judith S. Ford, QA Manager for AEERL, is the Project Officer for the
QA contract with Research Triangle Institute.
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D.1.0 PROCEDURAL ELEMENTS
D.I.I Scope and Application
Organic compounds with boiling points of 300° C and higher, after extraction with
methylene chloride, evaporation of the solvent, and drying to constant weight, can be determined
quantitatively by the gravimetric analysis described in the procedure.1 This method is applicable
to organic liquids, solid sample extracts, aqueous extracts, and extracts from the Source
Assessment Sampling System (SASS) or Modified Method 5 train sorbent module. This analysis
should be performed after enough of the sample extract has been concentrated to weigh
accurately.2 The suggested solvent is methylene chloride because of its good extraction
properties and high volatility. Other solvents may give different results (e.g., methyl alcohol may
extract polar compounds which would not be extracted with methylene chloride). All samples
being dried to constant weight should be stored in a desiccator.
The range of applicability is limited by the sensitivity of the balance and the organic
content of the sample. The balance must be accurate to ± 0.01 mg. If a sample of five milliliters
is used for the analysis, then a sensitivity of 0.1 mg/5 mL or 0.002 mg/mL of sample can be
achieved. This sensitivity can be improved by further concentration of more sample.
D.1.2 Definitions
Method Blank: Provides a check on contamination resulting from sample
preparation and measurement activities. Typically run in the
laboratory after receipt of samples from the field by
preparing a material known not to contain the target
parameter. Addresses all chemicals and reagents used in a
method.
Reagent Blank: Provides information on contamination due to specific
chemical reagents used during sample preparation, plus any
background from the measurement system.
D-l
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Audit Sample: Has known "true values," but is flagged for the laboratory as a
"performance evaluation (PE) sample." Provides information on
performance, but this information must be tempered with the
understanding that the sample may be given extra attention by the
analyst. An internal PE sample is created by the in-house analytical
laboratory, while an external PE sample is created outside of the
analytical laboratory.
D.1.3 Interferences
Results may be biased due to contamination of the solvent, glassware, or both. A method
blank (control) shall be run in duplicate for each lot of solvent and/or set of samples to provide a
control check on the purity of the solvent and the glassware cleaning procedure. The method
blank, consisting of a solvent sample from the same lot as that used to prepare samples, shall be
prepared and concentrated in an identical manner.
Two reagent blanks shall be analyzed each day samples are run to ensure results which are
not biased due to solvent contamination. The reagent blank shall be a solvent sample from the
same lot used to prepare the samples and shall not be concentrated prior to analysis. To minimize
error in weight due to moisture condensation, the pans containing the sample must appear visually
dry before being placed in a desiccator in preparation for drying to constant weight.
D.I.4 Apparatus
(1) Analytical Balance: Capable of weighing 0.01 mg with an accuracy of ± 0.005 mg.
(2) Desiccating Cabinet: Seal-tight gasketed with gum rubber. (Desiccators which
use silicone sealant shall not be used because of possible contamination of the
sample. Silicone grease may interfere with subsequent analysis.)
(3) Oven: Capable of operation to 175°C.
(4) Fume Hood: Standard laboratory.
D-2
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(5) Dust Cover. Plexiglass®, or equivalent: To protect samples drying in hood.
D.I.5 Reagents and Materials
(1) Disposable Aluminum Weighing Pans: Approximately 2" in diameter, 1/2" deep;
crimped sides; weighing approximately 1.0 grams.
(2) Tweezers.
(3) Aluminum Foil
(4) Pipets: 1 to 5 mL (Class A Volumetric).
(5) Glass Beakers: 50 to 400 mL.
(6) Wash Bottles: Teflon® or equivalent.
(7) Deionized Water.
(8) Nitric Acid/Sulfuric Acid. 50:50 (V/V): Prepared from reagent-grade acids.
(9) Methylene Chloride: Burdick and Jackson or equivalent grade.
(10) Methyl Alcohol: Burdick and Jackson or equivalent grade.
(11) Drierite® and/or Silica Gel: New Drierite® or silica gel may be used as received.
Used Drierite® or silica gel may be reactivated by drying it in an oven for at least
two hours at 175°C.
D.I.6 Sample Handling
All apparatus that contacts either the concentrated or evaporated residue samples shall be
glass, Teflon®, aluminum, or stainless steel. Evaporation of samples shall be carried out in an
area free of airborne dust and organic vapors that could contaminate the samples.
Ordinarily, all glassware coming in contact with a sample, in either dilute or concentrated
form, must be cleaned by complete Level 1 procedures.2 Briefly, this cleaning procedure entails
D-3
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sequential cleaning with soapy water, deionized water, 50:50 (V/V) nitric acid:sulfuric acid,
deionized water, methyl alcohol, and methylene chloride, followed by oven drying. The use of
deionized water for cleaning glassware is critical when inorganic substances are being analyzed or
heavy metal contaminants are present in high concentration in tap water.
This ROP, however, covers only the analysis of organic constituents. Tap water can be
substituted for deionized water in glassware cleaning whenever the organic concentration exceeds
1 mg/sample as measured by this ROP. Experience has shown that tap water adds no measurable
amount of organic contaminants to the method or reagent blanks under these conditions.
D.I.7 Sampling/Analysis Procedures
(1) Label aluminum sample pans on the underside using a ballpoint pen or other sharp
object. Handle dishes only with clean tweezers.
(2) Clean the weighing pans by first rinsing them with deionized water, then dipping
them successively into three beakers of methyl alcohol, methylene chloride, and,
finally, methyl alcohol again.
(3) Dry the cleaned weighing pans to constant weight on a shelf lined with clean
aluminum foil in an oven heated to at least 105°C. Cool the plans in a desiccator
for a minimum of 4 to 8 hours or overnight.
(4) Weigh pans to constant weight to an accuracy of ± 0.01 mg, recording the pan tare
weight.
(5) By pipet, transfer a 1.0 mL aliquot of the sample to the aluminum sample pan or
use 1/10 of the concentrated sample. Aliquot size must never exceed 5 mL to
avoid loss of sample through capillary action.
(6) Place the sample pan on a clean piece of aluminum foil in a clean fume hood.
Shield the pan from dust with a Plexiglas® or other cover positioned to allow for
adequate air circulation. Evaporate sample to visual dryness at room temperature.
Solvent evaporation usually takes about 30 minutes.
(7) Place sample pan in desiccator over Drierite® and/or silica gel for at least 8 hours.
D-4
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(8) Weigh sample pan at approximately 4-hour intervals until three successive values
differ by no more than ± 0.03 mg. If the residue weight is less than 0.1 mg,
concentrate more sample in the same sample pan. If there is insufficient sample
remaining for this purpose, report the initial value obtained, along with an
explanation.
D.1.8 Calculations
The gravimetric range organics (GRAY) is calculated in units of mg/sample as follows:
(Sample Weight + Pan Weight ) - (Pan Tare Weight )
GRAY =
rng
Aliquot Volume T /Total Concentration Sample Volume
The calculated GRAV weight is corrected for the method blank:
Corrected GRAV mass = Measured GRAV mass - Method Blank mass
D.1.9 Data Reporting
The results of the analysis are averaged and reported in units of mg organics/original
sample.
D.I.10 Precision
Duplicate analyses shall be run by the same analyst and shall be rejected if results differ by
more than 20% from the average. If insufficient material is present to rerun the sample, both
values will be reported with a qualifying statement.
D-5
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D.I.11 Accuracy
Dry sample weight should be at least 1 mg per analysis whenever possible. Accuracy of
the analysis is ± 20% of actual value. A proficiency test should be performed by each analyst as
described in Section 2.0.
D.2.0 QUALITY CONTROL ELEMENTS
All operators should demonstrate proficiency with Gravimetric Analysis of Organic
Extracts (GRAY) prior to sample analysis. In the proficiency testing, include a
GRAY analysis of a reagent blank, a method blank, and an audit sample. The
method or reagent blank shall be less than 5 mg/niL of sample. Results of the
audit sample shall be within the precision and accuracy specifications outlined in
this ROP.
Two types of audit samples are used. The first contains 100 mg of eicosane
[CH3(CH2)18CH3] in 250 mL of methylene chloride. Concentrate this solution to
10 mL in a manner identical to that used for sample preparation prior to GRAY
analysis. The second type of audit sample can be either prepared in-house or
received from an independent laboratory. An external audit sample must contain
organic compounds with chain lengths of more than 18 carbons (and boiling points
above 300°C) in sufficient concentration to be determined accurately. Perform the
GRAY analysis in duplicate as described in Section 1.7 of this procedure.
Determine the GRAY value of duplicate method blanks for each new lot of solvent
and/or set of samples. Run a method blank any time contamination is suspected.
Prepare the blank using the same lot of reagent and the same concentration
procedure as that used to prepare the samples. The solvent sample shall be a
volume equivalent to that used for sample preparation. If the blank GRAY value is
unusually high (i.e., 5 mg/mL of sample), find the cause of the contamination and
repeat the method blank GRAY analysis.
Analyze two reagent blanks for GRAY each day samples are run to ensure the
results are not biased due to solvent contamination. The reagent blank shall
consist of an aliquot of the solvent used to prepare the samples. If both reagent
blank GRAY values are high (i.e., 2 mg/mL of sample), find the cause of the
contamination and reanalyze samples and reagent blanks.
D-6
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Analyze all samples in duplicate. Samples are analyzed by the same analyst and
must agree to within 20% of the average. In the event this condition is not met,
repeat the analyses.
NOTE: If the conditions require the sample to be reanalyzed (e.g., high
blank values or poor precision) and insufficient sample remains,
then report the value obtained by the initial analysis and include a
qualifying statement.
D-7
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The following section (D.3.0, MicroGRAV) is a supplement to the original GRAY SOP,
dated 9/86 3
D.3.0 MICROGRAV
The microGRAV technique allows the analyst to use a lighter gravimetric weigh pan and a
smaller aliquot of sample extract to perform the extract weighings. All of the procedures used in
traditional GRAY analysis are used with the following exceptions:
D.3.1 Reagents and Materials
(1) Weigh pans: Disposable weigh pans are constructed using heavy duty aluminum
foil and a molding jig similar to the one shown in Figure D-l. The jig may be
constructed of any inert material (nylon, plastic, Teflon®), providing it conforms
to the general shape of the figure and the internal surfaces have generally rounded
edges for ease of molding. The foil is cut into 2 inch circles or squares of foil,
molded into shape by hand pressing, and the excess foil is cut away from the outer
edges of the pan with a sharp knife or scissors. This produces pans weighing
approximately 0.25 grams each, replacing the commercial 1 gram weigh pans.
(2) Pipets: Positive displacement pipets, fixed volume 250 jiL or adjustable volume
100-250 jiL are recommended (Rainin Pipetman® or equivalent with a Teflon®
plunger internal to the pipet). Disposable tips are used as received from the
manufacturer, one per sample extract.
D.3.2 Sampling/Analysis Procedures
(1) Label aluminum foil pans by marking on the underside using a dull pencil or
toothpick. Use caution to avoid piercing through the pan.
(2) There is no need to clean the pans with solvent as long as they are kept from
contact with excess dust or moisture. Experience has shown that the homemade
pans are quite free of organic contamination indicated by the analysis of many
solvent and dust blanks.
D-8
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1/2
inch
2 inches
EC
o
o
in
Figure D-l. Molding Jig for Construction of MicroGRAV Pans
D-9
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(3) The pans are ready to use after molding and desiccating prior to tare weighing.
No preheating or drying with an oven is necessary.
(4) Using a positive displacement disposable pipet, transfer a 0.250 mL aliquot of
sample to the microGRAV pan. If necessary for a specialized application requiring
larger aliquots, repeated transfers of 0.250 mL can be added to an individual pan,
allowing the extract to air dry in the fume hood between transfers.
(5) All other procedures of microGRAV analysis are identical to the traditional GRAY
techniques: carefully handle the pans with tweezers, air dry to visual dryness in a
protective fume hood prior to desiccating, weigh the sample with a manual or
digital microbalance, perform mass calculations, etc.
D.4.0 REFERENCES
1. Harris, J.C. et al. Laboratory Evaluation Level 1 Organic Analysis Procedure.
EPA-600/S7-82-048, NTIS PB 82-239, pp. 30-36, March 1982.
2. Lentzen, D.E., D.E. Wagoner, E.D. Estes, and W.F. Gutknecht. IERL Procedures
Manual: Level 1 Environmental Assessment (Second Edition). EPA-600/7-78-
201, NTIS PB 293-795, pp. 26-142, October 1978.
3. Assisting in the preparation of this supplement, dated 9/91 were Robert F. Martz
and David F. Natschke of Acurex Environmental Corporation, Research Triangle
Park, NC, under EPA contract 68-02-4701 in support of the multi-laboratory
Boise and Roanoke Integrated Air Cancer Program. James Dorsey and Raymond
Steiber of EPA were the technical directive managers for the EPA contract with
Acurex Environmental. Judith S. Ford was the EPA QA Manager of record for
the AEERL contract.
D-10
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Appendix E
EPA Method 0040
Sampling of Principal Organic Hazardous Constituents from Combustion
Sources Using Tedlar Bags
This method was proposed as part of the Third Update to the SW-846 Methods Manual in July of
1995. At the time of this writing (5/15/97), promulgation of the final version of the method is
expected within weeks. Please contact MICE at 703-821-4690 (or e-mail to
mice@lan828.ehsg.saic.com) for the most recent version of Method 0040.
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Appendix F
EPA Method 0010
Modified Method 5 Sampling Train
This method was promulgated as part of the 3rd Edition of the SW-846 Methods Manual, for
which the complete citation is:
Test Methods for Evaluating Solid Waste, Physical/Chemical Methods, SW-846 Manual,
3rd ed^ Document No. 955-001-000001. Available from Superintendent of Documents,
U.S. Government Printing Office, Washington, DC, November 1986.
The full document is available from U. S. Government Printing Office, telephone 202-783-3238,
or on CD-ROM from National Technical Information Center at 703-487-4650 (or at
http://www.ntis.gov).
For individual methods, or information about the methods, call MICE at 703 821-4690 (or e-mail
to mice@lan828.ehsg.saic.com).
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Appendix G
EPA Method 3542
Preparation of Modified Method 5 (SW-846, Method 0010)
Train Components for Analysis by SW-846 Method 8270
This method was proposed as part of the Third Update to the SW-846 Methods Manual in July of
1995. At the time of this writing (5/15/97), promulgation of the final version of the method is
expected within weeks. Please contact MICE at 703-821-4690 (or e-mail to
mice@lan828.ehsg.saic.com) for the most recent version of Method 3542.
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