EPA/625/R-96/010a
Compendium of Methods
for the Determination of
Inorganic Compounds
in Ambient Air
Compendium Method IO-3.4
DETERMINATION OF METALS
IN AMBIENT PARTICULATE
MATTER USING INDUCTIVELY
COUPLED PLASMA (ICP)
SPECTROSCOPY
Center for Environmental Research Information
Office of Research and Development
U.S. Environmental Protection Agency
Cincinnati, OH 45268
June 1999
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Method IO-3.4
Acknowledgements
This Method is a part of Compendium of Methods for the Determination of Inorganic Compounds in
Ambient Air (EPA/625/R-96/010a), which was prepared under Contract No. 68-C3-0315, WA No. 2-10,
by Midwest Research Institute (MRI), as a subcontractor to Eastern Research Group, Inc. (ERG), and
under the sponsorship of the U.S. Environmental Protection Agency (EPA). Justice A. Manning, John O.
Burckle, Scott Hedges, Center for Environmental Research Information (CERI), and Frank F. McElroy,
National Exposure Research Laboratory (NERL), all in the EPA Office of Research and Development, were
responsible for overseeing the preparation of this method. Other support was provided by the following
members of the Compendia Workgroup:
• James L. Cheney, U.S. Army Corps of Engineers, Omaha, NE
Michael F. Davis, U.S. EPA, Region 7, KC, KS
Joseph B. Elkins Jr., U.S. EPA, OAQPS, RTP, NC
Robert G. Lewis, U.S. EPA, NERL, RTP, NC
Justice A. Manning, U.S. EPA, ORD, Cincinnati, OH
• William A. McClenny, U.S. EPA, NERL, RTP, NC
Frank F. McElroy, U.S. EPA, NERL, RTP, NC
• William T. "Jerry" Winberry, Jr., EnviorTech Solutions, Gary, NC
This Method is the result of the efforts of many individuals. Gratitude goes to each person involved in the
preparation and review of this methodology.
Author(s)
• William T. "Jerry" Winberry, Jr., EnviroTech Solutions, Gary, NC
Peer Reviewers
Dewayne Ehman, Texas Natural Resource Conservation Committee, Austin, TX
• David Harlos, Environmental Science and Engineering, Gainesville, FL
• Doug Duckworth, Lockheed-Martin Energy Research, Oak Ridge, TN
Lauren Drees, U.S. EPA, NRMRL, Cincinnati, OH
DISCLAIMER
This Compendium has been subjected 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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Method IO-3.4
Determination of Metals in Ambient Particulate Matter Using
Inductively Coupled Plasma (ICP) Spectroscopy
TABLE OF CONTENTS
1. Scope 3.4-1
2. Applicable Documents 3.4-2
2.1 ASTM Standards 3.4-2
2.2 Other Documents 3.4-2
3. Summary of Method 3.4-2
3.1 Instrument Description 3.4-2
3.2 Sample Extraction 3.4-3
3.3 Sample Analysis 3.4-3
4. Significance 3.4-3
5. Definitions 3.4-4
6. Ranges, Sensitivities, and Detection Limits 3.4-5
7. Precision and Accuracy 3.4-6
8. Interferences 3.4-6
8.1 Spectral Interferences 3.4-6
8.2 Matrix Interference 3.4-7
9. Apparatus 3.4-7
10. Reagents 3.4-8
11. Analysis 3.4-9
11.1 Standard Stock Solutions 3.4-9
11.2 ICP Operating Parameters 3.4-10
11.3 Instrumental Preparations 3.4-10
11.4 Sample Receipt in the Laboratory 3.4-11
11.5 ICP Operation 3.4-11
12. Data Processing 3.4-13
12.1 Filter Blanks and Discrimination Limit 3.4-13
12.2 Metal Concentration in Filter 3.4-13
13. Quality Assurance 3.4-14
13.1 Instrumental Tuning and Standardization 3.4-14
13.2 Calibration For Quantitative Analysis 3.4-14
13.3 Daily QA Check and Analytical Run Sequence 3.4-14
13.4 Corrective Actions 3.4-16
13.5 Routine Maintenance 3.4-16
14. Method Safety 3.4-17
15. References 3.4-17
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IV
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Chapter IO-3
CHEMICAL SPECIES ANALYSIS
OF FILTER-COLLECTED SPM
Method IO-3.4
DETERMINATION OF METALS IN AMBIENT PARTICULATE MATTER USING
INDUCTIVELY COUPLED PLASMA (ICP) SPECTROSCOPY
1. Scope
1.1 Suspended participate matter (SPM) in air generally is a complex multi-phase system consisting of all
airborne solid and low vapor pressure liquified particles having aerodynamic particle sizes ranging from below
0.01-100 um and larger. Historically, SPM measurement has concentrated on total suspended particulates
(TSP), with no preference to size selection.
1.2 On July 1, 1987, the U. S. Environmental Protection Agency (EPA) promulgated a new size-specific air
quality standard for ambient particulate matter. This new primary standard applies only to particles with
aerodynamic diameters <10 um (PM10) and replaces the original standard for TSP. To measure concentrations
of these particles, the EPA also promulgated a new federal reference method (FRM). This method is based on
the separation and removal of non-PM10 particles from an air sample followed by filtration and gravimetric
analysis of PM10 mass on the filter substrate. In 1997, the PM10 standard was replaced with the national
ambient air quality standard (NAAQS) for PM2 5.
1.3 The new primary standard (adopted to protect human health) limits PM25 concentrations to 50 ug/m3,
averaged over a 24-h period. These smaller particles are able to reach the lower regions of the human
respiratory tract and, therefore, are responsible for most of the adverse health effects associated with suspended
particulate pollution. The secondary standard, used to assess the impact of pollution on public welfare, has also
been established at 15 ug/m3 for an annual average.
1.4 Ambient air SPM measurements are used (among other purposes) to determine whether defined
geographical areas are in attainment or non-attainment with the NAAQS for PM2 5. These measurements are
obtained by the states in their state and local air monitoring station (SLAMS) networks as required under 40CFR
Part 58. Further, Appendix C of Part 58 requires that the ambient air monitoring methods used in these EPA-
required SLAMS networks must be methods that have been designated by EPA as either reference or equivalent
methods.
1.5 The procedure for analyzing the elemental metal components in ambient air particulate matter collected on
high volume filter material is described in this method. The high volume filter material may be associated with
either the TSP or PM10 sampler, as delineated in Inorganic Compendium Method IO-2.1.
1.6 Filters are numbered, pre-weighed, field deployed and sampled, returned to the laboratory, extracted using
microwave or hot acid, then analyzed by inductively coupled plasma (ICP) spectroscopy. The extraction
procedure is accomplished by following Inorganic Compendium Method IO-3.1.
1.7 This method should be used by analysts experienced in the use of ICP, the interpretation of spectral and
matrix interferences and procedures for their correction. A minimum of 6-months experience with commercial
instrumentation is required.
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Method IO-3.4 Chapter IO-3
ICP Methodology Chemical Analysis
1.8 Those metals and their associated method detection limit (MDL) applicable to this technology are listed in
Table 1.
2. Applicable Documents
2.1 ASTM Standards
• D1356 Definition of Terms Related to Atmospheric Sampling and Analysis.
• D1357 Planning the Sampling of the Ambient Atmosphere.
• D4096 Application of the High Volume Sample Method for Collection and Mass Determination of
Airborne Particle Matter.
2.2 Other Documents
• U. S. Environmental Protection Agency, Quality Assurance Handbook for Air Pollution
Measurement Systems, Volume I: A Field Guide for Environmental Quality Assurance, EPA-600/R-
94/03 8a.
• U. S. Environmental Protection Agency, Quality Assurance Handbook for Air Pollution
Measurement Systems, Volume II: Ambient Air Specific Methods (Interim Edition),
EPA-600/R-94/038b.
• Reference Method for the Determination ofParticulate Matter in the Atmosphere, 40 CFR 50,
Appendix J.
• Reference Method for the Determination of Suspended Particulates in the Atmosphere (High
Volume Method), 40 CFR 50, Appendix B.
• Reference Method for the Determination of Lead in Suspended P articulate Matter Collected from
Ambient Air, Federal Register 43 (194): 46258-46261.
• U. S. EPA Project Summary Document (1).
• U. S. EPA Laboratory Standard Operating Procedures (2).
• Scientific Publications of Ambient Air Studies (3-7).
3. Summary of Method
3.1 Instrument Description
3.1.1 The analytical system is an inductively coupled plasma atomic emission spectrometer, as illustrated
in Figure 1. The plasma is produced by a radio frequency generator. The current from the generator is fed
to a coil placed around a quartz tube through which argon flows. The oscillatory current flowing in the coil
produces an oscillating magnetic field with the lines of force aligned axially along the tube. The argon is
seeded with electrons by momentarily connecting a Tesla coil to the tube where the plasma forms inside. The
ions in the gas tend to flow in a circular path around the lines of force of the oscillatory magnetic field and
the resistance to their flow produces the heat. To avoid melting the silica tube, a flow of argon is introduced
tangentially in the tube, which centers the plasma away from the walls of the tube. The plasma is formed in
the shape of a toroid or doughnut, and the sample is introduced as an aerosol through the middle of the toroid.
The hottest part of the plasma is in the ring around the center of the toroid, where temperatures of about
10,000 K are achieved. Through the center of the toroid where the sample is introduced, the temperature
is somewhat lower, and the sample is subjected to temperatures of about 7,000 K. From the very hot region
in the plasma and just above it, a continuum is radiated because of the high electron density. Above this
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Chapter IO-3 Method IO-3.4
Chemical Analysis ICP Methodology
region, the continuum emission is reduced as the temperature falls and the spectral lines of the elements in
the sample may be observed. Since this plasma is generated in an inert atmosphere, few chemical
interferences exist.
3.1.2 The spectrum is resolved in a spectrometer. The relative intensities and concentrations of the
elements are calculated by a small computer or processor. Samples containing up to 61 preselected elements
can be analyzed by ICP simultaneous analysis at a rate of 1 sample per minute. The ICP technique can
analyze a large range of concentrations. A single calibration curve can accomodate changes in concentration
of 5 orders of magnitude.
3.2 Sample Extraction
Two extraction procedures may be performed: hot acid extraction or microwave extraction, as documented
in Inorganic Compendium Method 10-3.1. Extraction involving hot acids is hazardous and must be
performed in a well-ventilated fume hood.
3.3 Sample Analysis
A technique for the simultaneous or sequential multi-element determination of trace elements in an acid
solution is described in this Compendium method (see Figure 2). The basis of the method is the measurement
of atomic emission by an optical spectroscopic technique. Samples are nebulized and the aerosol that is
produced is transported to the plasma torch where excitation occurs. Characteristic atomic-line emission
spectra are produced by a radio frequency ICP. The spectra are dispersed by a grating spectrometer, and
the intensities of the line are monitored by photo multiplier tubes. The photo currents from the photo
multiplier tubes are processed and controlled by a computer system. A background correction technique is
required to compensate for variable background contribution to the determination of trace elements.
Background must be measured adjacent to analyte lines on samples during analysis. The position selected
for the background intensity measurement, on either or both sides of the analytical line, will be determined
by the complexity of the spectrum adjacent to the analyte line. The position used must be free of spectral
interference and reflect the same change in background intensity as occurs at the analyte wavelength
measured. Data is processed by computer and yields micrograms of metal of interest per cubic meter of air
sampled (p.g/m3).
4. Significance
4.1 The area of toxic air pollutants has been the subject of interest and concern for many years. Recently,
the use of receptor models has documented the need for elemental composition of atmospheric aerosol into
components as a means of identifying their origins. The assessment of human health impacts, resulting in
major control actions by federal, state, and local governments, is based on these data. Accurate measures
of toxic air pollutants at trace levels are essential for proper assessments. The advent of inductively coupled
plasma spectroscopy has improved the speed and performance of metals analysis in many applications.
4.2 ICP spectroscopy is capable of quantitatively determining most metals at levels that are required by
federal, state, and local regulatory agencies. Sensitivity and detection limits may vary from instrument to
instrument.
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Method IO-3.4 Chapter IO-3
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5. Definitions
[Note: Definitions used in this method are consistent with ASTM methods. All pertinent abbreviations and
symbols are defined within this document at point of use.]
5.1 Autosampler. Device that automatically sequences injections of sample solutions into the ICP.
5.2 Background Correction. Removing a high or variable background signal, using only the peak height
of intensity for calculating concentration. Instruments measure background at one or more points slightly
off the emission wavelength and subtract the intensity from the total intensity measured at the analytical
wavelength.
5.3 Channels. Simultaneous ICPs have an array of photo multiplier tubes positioned to look at a fixed set
of elements (wavelengths); each wavelength is a "channel," which varies by instrument.
5.4 Detection Limits. Determined by calibrating the ICP and determining the standard deviation of apparent
concentrations measured in pure water. The result (a) is multiplied by a factor from 2 to 10 (usually 3) to
define a "detection limit." Complex sample matrices result in a higher background noise than pure water,
so actual detection limits vary considerably with sample type. It is recommended that an instrument detection
limit (IDL) be determined in a standard whose concentration is about three times the expected detection limit.
5.5 Detectors. Photomultiplier tubes (PMTs).
5.6 Fixed Optics. The most crucial element in the optical design. If the grating moves during measurement,
uncertainties in the results are inevitable.
5.7 Grating. The optical element that disperses light.
5.8 Integration Time. The length of time the signal from the PMT is integrated for an intensity
measurement. The most precise measurements are taken at the peak intensity.
5.9 Inter Element Intereference. When emission lines from two elements overlap at the exit slit, light
measured by the PMT is no longer a simple measure of the concentration of one element. The second
element interferes with the measurement of the first at that wavelength. If lines free of interference can't be
found, approximate concentrations of the element of interest can be calculated by calibrating that element and
the interferent (inter element correction).
5.10 Linear Dynamic Range. The light intensity in an ICP source varies linearly with the concentration of
atoms over more than 6 orders of magnitude (the linear dynamic range). This variation allows for
determination of trace and major elements in a single sample, without dilution. Fewer standards for
calibration are needed, often a high standard and a blank suffice.
5.11 Limit of Quantitation. The lowest level at which reliable measurements can be made. Defined as ten
times the standard deviation of a measurement made in a blank (pure water), which is 3.3 times the "3a"
detection limit.
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Chapter IO-3 Method IO-3.4
Chemical Analysis ICP Methodology
5.12 Monochromator. The spectrometer design on a sequential ICP.
5.13 Nebulizer. A device creating a fine spray of sample solution to be carried into the plasma for
measurement. Its performance is critical for good analyses.
5.14 Photomultiplier Tubes (PMTs). Light detectors in ICP instruments. When struck by light, the PMT
generates a current proportional to the intensity.
5.15 Polychromator. The spectrometer design of a simultaneous ICP.
6. Ranges, Sensitivities, and Detection Limits
6.1 Sensitivity, instrumental detection limit, precision, linear dynamic range, and interference effects must
be investigated and established for each individual analyte line on a particular instrument. All measurements
must be within the instrument linear range where correction factors are valid. The analyst must verify that
the instrument configuration and operating conditions satisfy the analytical requirements and to maintain
quality control data, i.e., confirming instrument performance and analytical results.
6.2 For comparison, Table 1 provides typical maximum element concentrations obtained on a Thermo Jarrell
Ash Model 975 Plasma AtomComp ICP.
6.3 Calibration sensitivities are dependent upon spectral line intensities. For comparison, Table 1 provides
typical sensitivities for the ICP mentioned in Section 6.2 for a Jarrell Ash Model 975 Plasma AtomComp ICP.
6.4 Detection limits vary for various makes and models. Typical detection limits achievable by the Thermo
Jarrell Ash Model 975 ICP are given in Table 1. These are computed as 3.3 times the standard deviation of
the distribution of outputs for the repeated measurement of a standard, which contains no metals and is used
as the zero point for a two-point instrument standardization described in Section 11.3. The acid
concentrations of this standard must match the acid concentrations of blanks and samples.
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Method IO-3.4 Chapter IO-3
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7. Precision and Accuracy
7.1 Accuracy for this procedure has not been determined. Spiked strips used for audits have been developed
by the EPA. The main use of the audit results is to document chronologically the consistency of analytical
performance. One multi-element audit sample should be extracted daily with normal ambient air samples.
Audit samples can only approximate true atmospheric particulates, which contributes to the overall
uncertainty. Attempts should be made to use National Institute of Standards and Technology (NIST) 1648
(urban particulate) to judge recovery. This material is not ideal because (1) there is no filter substrate;
(2) relatively large amounts (100 mg) are required to overcome problems of apparent inhomogeneity, which
in turn necessitates dilutions not required in normal application of this method; and (3) element ratios differ
somewhat from those found in real samples. Typical recoveries experienced with the spiked strips and
NIST 1648 are presented in Table 2.
7.2 Typical precision, bias, and correlation coefficients calculated from audit samples vs. blind replicate
analyses are shown in Table 3. Treatment of the glass fibers during filter manufacture affects both recovery
and precision of sample replicate pairs. This fact should be considered when studies are designed.
7.3 Good precision data does not imply accuracy; bias is still possible. Bias is nearly impossible to detect
when a given type of sample is always analyzed by the same method using the same instrumentation. In this
method, bias, if any, is most likely to arise during the sampling and sample preparation steps.
7.4 Quality assurance (QA) activities are discussed in Section 13 of this method. QA data for the method
are composed of QA data for the instrument and for the sampling and sample preparation steps. The former
are relatively easy to obtain by the analysis of known solutions and are usually quite good because of the
inherent stability and linearity of the plasma and associated electronics. QA data for the sampling and sample
preparation steps are nearly always poorer than for the instrument and thus dictate the QA data for the
method as a whole. Consequently, a good instrumental calibration does not guarantee that the data produced
are accurate. For instance, independent analysis (by neutron activation analysis) of real samples and of NIST
SRM 1648 has revealed that Cr and Ti extractions are 25-75% efficient using the method described herein,
yet both elements in solution are recovered very well by the plasma instrument.
8. Interferences
8.1 Spectral Interferences
Spectral interferences result when spectrally pure solutions of one element produce a finite output on channels
assigned to other elements. Table 4 provides recommended wavelengths to monitor selected metals using
ICP in order to minimize spectral interferences. When the quantitative correction is made, the order of
correction is arranged so that only "true" (that is, interference-free or previously corrected) values are used
in any quantitative correction of another element for comparison. The quantitative correction factors are
listed in Table 10 in the order in which they are applied in the data-processing step for the analysis of ambient
air using the Thermo Jarrell Ash Model 975 ICP. The correction relation for any affected element is:
„. „ . .. (apparent cone.)-(correction factor "true")
true concentration = -^-t-i- '—
(concentration of the affecting element)
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Chapter IO-3 Method IO-3.4
Chemical Analysis ICP Methodology
[Note: The information in Table 10 was generated using a specific instrument and is presented only to provide
an indication of potential interferences. Specific correction factors must be generated for each instrument
during each analysis.]
8.2 Matrix Interference
Matrix interferences do exist. This problem has been minimized by matrix matching of standards and
samples. Matrix interferences depend on the types and quantities of acids used; element emission lines may
be enhanced or depressed. These interferences may be circumvented by careful matrix matching of
standards, QC solutions, and samples. Careful matches were made in the development of this procedure.
9. Apparatus
[Note: This method was developed using the Thermo Jarrell Ash Model 975 Plasma AtomComp, 27 Forge
Parkway, Franklin, MA 02038, (508) 520-1880, as a guideline. EPA has experience in use of this equipment
during various field monitoring programs over the last several years. Other manufacturers' equipment should
workas well. However, modifications to these procedures may be necessary if another commercially available
sampler is selected.]
9.1 Desiccator. For cooling oven-dried chemicals.
9.2 Gravity Convection Type Drying Oven. Drying chemicals and glassware, Precision Scientific 31281
or equivalent.
9.3 Mechanical Convection Type Drying Oven. For drying plastic ware (Blue Island Electric 0V 510A-2
or equivalent).
9.4 Inductively Coupled Plasma Emission Spectrometer. The ICP described in this method is the Thermo
Jarrell Ash Model 975 Plasma AtomComp, 27 Forge Parkway, Franklin, MA 02038, (508) 520-1880. EPA
has experience in use of this equipment during various field monitoring programs. Other manufacturers'
equipment should work as well. The instrument uses a Plasma Therm HFS 2000D R.F. generator as the
power supply for the plasma. The excitation source is a three-turn inductively coupled plasma torch with a
cross-flow pneumatic nebulizer for sample introduction. Samples are pumped to the nebulizer with a Gilson
Minipuls II single channel peristaltic pump. The instrument is equipped to read 48 elements as identified in
Table 4. A dedicated PDP-8E (Digital Equipment Corporation) minicomputer controls the instrument and
yields a concentration printout. To achieve data storage capability, the PDP-8E has been interfaced with a
PDP11/34.
9.5 Bottles. Linear polyethylene or polypropylene with leakproof caps for storage of samples. (500 mL,
125 mL, and 30 mL). Teflon bottles for storing multi-element standards.
9.6 Pipettes. Volumetric 50 mL, 25 mL, 20 mL, 15 mL, 10 mL, 9 mL, 8 mL, 7 mL, 6 mL, 5 mL, 4 mL,
3 mL, 2 mL, Class A borosilicate glass.
9.7 Pipettes. Graduated 10 mL, Class A Borosilicate glass.
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Method IO-3.4 Chapter IO-3
ICP Methodology Chemical Analysis
9.8 Pipette. Automatic dispensing with accuracy of 0.1 mL or better and repeatability of 20 ,uL (Grumman
Automatic Dispensing Pipet, model ADP-30DT, or equivalent).
10. Reagents
10.1 Hydrochloric Acid. Ultrex grade, 12.3 M (Baker 1-4800) for preparing standards.
10.2 Nitric Acid. ACS reagent grade, concentrated (16 M) for preparing 10% v/v nitric acid, to clean
labware only (Fisher A-200). Add 100 mL of concentrated HN03 to ~ 500 mL of ASTM Type II water and
dilute to 1 L.
[Note: This acid is not for sample preparation; it contains excessive metals].
10.3 Nitric Acid. Ultrex grade, 16 M (Baker 1-4801) for preparing standards.
10.4 Stock Calibration Standards. Multi-element and single-element plasma-grade stocks are used for the
analysis. The stocks are purchased from Spex Industries, Inc., Inorganic Ventures, Inc., or equivalent.
Working calibration standards are prepared by dilution of the concentrated calibration stocks. The calibration
standard stocks used for instrument calibration and initial calibration verification (ICV) are purchased from
different suppliers. The source (manufacturer and lot), concentration, expiration date, and acid matrix are
recorded for all calibration standards used for the analysis. Stock solutions should be stored in Teflon bottles.
The final concentration of nitric and hydrochloric acid in the calibration standards should be the same as those
in the prepared samples.
10.5 Compressed Argon in Cylinders and Liquid Argon in Tanks, Purity 99.95%. Best source.
10.6 ASTM Type I water (ASTM D1193). Best source. The Type I water should have a minimum
resistance of 16.67 milli-ohms, as evidenced by the reading of the resistivity meter during water flow.
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Chapter IO-3 Method IO-3.4
Chemical Analysis ICP Methodology
11. Analysis
11.1 Standard Stock Solutions
11.1.1 All labware should be scrupulously cleaned. The following procedure is recommended: Wash
with laboratory detergent or ultrasonic for 30 min with laboratory detergent. Rinse and soak a minimum of
4 hr in 10% V/V nitric acid. Rinse 3 times with deionized, distilled water, and oven dry.
[Note: Nitric and hydrochloric acid fumes are toxic. Prepare in a well-ventilated fume hood. Mixing results
in an exothermic reaction. Stir slowly.]
11.1.2 Preparing Calibration Curve Standards. Mixed calibration curve standards are prepared by
diluting appropriate volumes of the stock calibration standards in Class A volumetric flasks. Table 1 provides
examples of typical concentrations used for calibration for several elements. Each working standard solution
should be labeled with a name, an expiration date, and the initials of the preparer.
11.1.3 Prepare Initial Calibration Verification Standard (ICV). The ICV standards are analyzed
immediately following initial calibration. The ICV standards are prepared at the midpoints of the calibration
curves. These standards are prepared from certified stocks having a different manufacturer than the
calibration standards. The final concentration of the ICV should be in the range of 25 p.g/mL for Al, Ca, Fe,
Mg, K and Na. All other analytes should be in the range of 2 p.g/mL.
11.1.4 Prepare Interference Check Standard (ICS). The interference check standards are analyzed at the
beginning and end of the sample run and for every 8 hours of continuous operation. The ICS should contain
approximately 200 p.g/mL of Al, Ca, Fe, and Mg. In addition, the ICS should contain approximately
1 p.g/mL of all other analytes, including Ag, Be, Ca, Cd, Co, Cr, Cu, Fe, Pb, Se T, Y, Zn, and Bi.
11.1.5 Laboratory Control Spike (LCS). An LCS is prepared and analyzed with each sample batch (or
1 per 20 samples). The LCS is prepared for all analytes at the 2 p-g/mL level and when analyzed, should be
within 80% to 120% of actual concentration. If the results are not within this criterion, then the results must
be qualified.
11.1.6 Matrix Spike (MS). A MS sample is prepared and analyzed with each sample batch (or 1 per
20 samples). These samples are used to provide information about the effect of the sample matrix on the
digestion and measurement methodology. The spike is added before the digestion, (i.e., prior to the addition
of other reagents). The MS should be at the 25 pg/strip level. The percent recovery for the analyte as part
of the MS should be between 75% and 125% for all analytes.
11.1.7 Prepare a Reagent Blank (RB). Prepare a reagent blank that contains all the reagents in the same
volumes used in processing the routine samples. The reagent blank must be carried through the entire
preparation procedure and analysis scheme. The final solution should contain the same acid concentration
as sample solutions for analysis. The running frequency of analysis of a reagent blank is about 1 for every
40 real samples.
11.2 ICP Operating Parameters
A daily log of the operating parameters should be maintained for reference. Entries are made by the analyst
of periodic intervals throughout the run. The following list of parameters are examples from the Thermo
Jarrell Ash Model 975 Plasma AtomComp. Specific manufacturer's guidelines should be followed.
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ICP HARDWARE SPECIFICATIONS
• Plasma power 1.1 kW forward automatic control
11 W reflected (minimum possible)
• Argon coolant flow 18 1/min liquid argon source
• Argon nebulizer flow 16 psi (approx. 700 mL/min)
• Sample uptake Avg. 1.85 mL/min
• Observation Zone Centered 16 mm above the load coil
• Sample preflush time 45 s; preburn, 1 s
• Exposure 10 s
• H20 Post Flush 10 s then proceed to next sample
• Slits 25-p.m entrance slit; 75-p.m exit slit
• Photomultiplier tube voltage 900 V
11.3 Instrumental Preparations
11.3.1 Calibration Curve Linearity. ICP spectrometers generally are considered to yield a linear
response over wide concentration ranges; however, investigation for linearity for elements expected to exceed
concentrations of about 25 p.g/mL may be necessary. Linearity may vary among manufacturers and
according to operating parameters. The method and conditions described in this procedure have imposed the
following limitations:
• Ca response is linear to 40 p.g/mL, becoming non-linear.
• Cr saturates the electronics at 50 p.g/mL.
• Cu saturates the electronics at 40 p.g/mL.
• Fe saturates the electronics at 230 p.g/mL.
• Mg response is curvilinear to 40 p.g/mL, becoming unuseable.
• Na response is curvilinear to 80 p.g/mL, becoming unuseable.
The curvilinear nature of Mg and Na responses below the levels specified were made acceptable by
programming the ICP computer with segmented calibration curves as described in the manufacturer's
instructions.
11.3.2 Spectral Interferences. Section 8 described briefly spectral interferences. A thorough
determination of spectral interferences is a lengthy, time-consuming study in itself. The following are some
of the factors influencing the presence or absence and magnitude of interferences:
• Wavelength of lines being read;
• Expected concentrations of the elements involved;
• Quality and the stability of the system optics (i.e., minimal deterioration with time);
• Quality and stability of photo multiplier tubes and electronics; and
• Purity of chemicals in use.
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A thorough study of interferences has been conducted by EPA in the development of this method and have
been addressed in the data processing program listed in Table 5.
[Note: The spectral interference factors listed in Table 5 were determined by analyzing single element
solutions of each interfering element. The concentration of each single element solution was within the linear
dynamic range (LDR) of the analysis, usually 100 ng/mL. The criteria for listing a spectral interference was
an apparent analyte concentration from the interfering single element solution that was outside the 95%
confidence interval estimates for the determined method detection limit (MDL) of the analyte. The factors are
presented as a guide for users of this method for determining interrelement interference effects. The user is
cautioned that other analytical systems other than the Thermo Jarrell Ash Model 975 Plasma AtomComp
described in this method may exhibit somewhat different levels of interference than those listed in Table 5 and
that the interference effects must be evaluated for each individual system.]
11.3.3 Matrix Interferences. Matrix interferences depend on the types and quantities of acids used;
element emission lines may be enhanced or depressed. These interferences may be circumvented by careful
matrix matching of standards, QC solutions, and samples. Careful matches should be made in the use of this
procedure.
11.4 Sample Receipt in the Laboratory
11.4.1 The sample should be received from the extraction laboratory in a centrifuge tube, as documented
in Inorganic Compendium Method 10-3.1.
11.4.2 No additional preservation is needed at this time. Sample is ready for ICP analysis.
11.5 ICP Operation
[Note: This method was developed using the Thermo Jarrell Ash 975 Plasma AtomComp spectrometer. EPA
has experience in the use of the Model 975 spectrometer associated with various field monitoring programs
involving analysis of filterable particulate matter for metals using ICP over the last several years. The use
of other manufacturers of ICP spectrometers should work as well as long as the quality assurance and quality
control specifications identified in Sections 13, Quality Control, are met. However, modifications to
Compendium Method 10-3.4 procedures may be necessary if another commercial ICP spectrometer is used.]
11.5.1 Start and allow the instrument at least 45 min for warmup.
11.5.2 Profile following manufacturer's directions. Run 12 warmup burns of old high QC solution to
exercise the photomultiplier tubes.
11.5.3 Standardize by opening the standardization buffers with a J command on the CRT operating
off-line from the PDP-11/34. Flush for 2 min with the first working standard. Make two exposures, print
the average ratio on the teletype, and identify the standard when queried. Repeat for all five working
standards. Complete with an S command and answer the query "Enter LCN" with a carriage return (RTN).
Calibration data are not stored in the PDP-11.
11.5.4 Go on-line to the PDP-11 by typing "RUN JA" and answer PDP-11 queries to identify the operator,
data storage, and operating condition codes.
11.5.5 The PDP-11 will automatically acquire gains and offsets (slopes and X-intercepts of the calibration
curve) determined by the ICP standardization. Values falling outside a previously determined bandwidth will
be reported by the computer. When this occurs, corrective action must be taken. Gain and offset values are
element-specific.
11.5.6 Measure the sample-pump uptake rate which should be approximately 1.8 mL/min.
June 1999 Compendium of Methods for Inorganic Air Pollutants Page 3.4-11
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Method IO-3.4 Chapter IO-3
ICP Methodology Chemical Analysis
11.5.7 Select a QC solution for analysis. On the CRT, enter RTN "QC" RTN "21", RTN for high QC,
or "QC" RTN "22", RTN for low QC. When "DSC" appears on CRT, type "HIQC" or "LOQC", as
applicable, followed by its prep date and RTN. The number "1.0" will appear twice, indicating the
multiplication and dilution factors have been set to 1.0. This step is followed by the query "OK?"
11.5.8 Begin pumping the QC solution selected in Section 11.5.7 from an aliquot. Start the stopwatch
when the leading edge of the solution has just entered the nebulizer. Time for 45 s and press RTN on the
CRT to begin the exposure. The end is signaled by the CRT bell. Transfer the pickup tube to deionized
distilled water.
11.5.9 When the PDP-11 has acquired the data, it will query "QCSMP:." Type RTN, "STD," RTN "21,"
RTN to identify the zero standard (Working Standard No. 1; see Section 11.1). After "DCS:" As in Section
11.5.7, the multiplication and dilution factors will default to 1.0, and the query "OK?" will appear.
11.5.10 Begin pumping from an aliquot of the zero standard and time for 45 s, as in Section 11.5.8. Start
the exposure with RTN on the CRT. At the bell, return the pickup to deionized, distilled water.
11.5.11 When the PDP-11 has acquired the data, it will query "STD SMP:." Type "1," RTN, RTN, and
it will query "OK?" Type "NO," RTN and the cursor will move to the left end of the line.
11.5.12 Select the first sample. On the CRT, enter the Project I.D. from the label. Press RTN. Type
numerical sample number and RTN. After "DCS:," type the four letter I.D. code and RTN. The computer
next queries "MLT:" (for multiplication factor); enter "360", RTN. After "DIL:" (for dilution factor), enter
"1," RTN. The computer then asks "OK?"
11.5.13 Begin pumping the sample from the sample bottle and time for 45 s before pressing RTN. At
the bell, return the pickup to deionized, distilled water and select the next sample.
11.5.14 Enter second sample by typing the sample number, RTN, 4-letter I.D., RTN, and another RTN
to begin the exposure.
11.5.15 Present 8 samples to the instrument.
11.5.16 Challenge the instrument with the QC solution that was not selected in Section 11.3.7. Repeat
CRT entries and procedure in Sections 11.5.7 and 11.5.8.
11.5.17 Resume sample analysis. Repeat Sections 11.5.11 through 11.5.13.
11.5.18 Analyze nine samples.
11.5.19 Return to Section 11.5.6 and repeat through Section 11.5.17.
11.5.20 End the analytical session after about 3 to 3.5 h. Type "-1," RTN. The computer will query "DO
YOU WISH TO SAVE THIS SESSION'S DATA?" Type "YES," RTN. The computer will back up the data
and issue instructions. This terminates the RUN JA program.
11.5.21 Usually two sessions per day are attempted. Repeat Sections 11.5.2 through 11.5.20 for the
second session.
11.5.22 Instrument operating parameters are recorded before and after every 20 burns. A typical day's
record is shown in Figure 3.
11.5.23 With minimal experience, the instrument operator will be able to compress the above steps (i.e.,
process more than one sample at a time by overlapping the steps required for the different samples).
12. Data Processing
12.1 Filter Blanks and Discrimination Limit
Since individual blanks are not available from each filter used for sampling, the mean unexposed filter value
is subtracted from the result for each exposed sample to obtain the best estimate of each element in the filter
particulate material. A discrimination limit must be defined so that possible contributions from an individual
filter are not falsely reported as being from the particulate material. Calculate the filter batch mean, Fm (see
Page 3.4-12 Compendium of Methods for Inorganic Air Pollutants June 1999
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Chapter IO-3 Method IO-3.4
Chemical Analysis ICP Methodology
Method 10-3.2), and the standard deviation of the Fm values for each filter. If Fm is greater than the
instrumental detection limit, then Fm must be subtracted from the total elemental content for each particulate
bearing filter when the net metal in the particulate material is calculated. Determine the smallest atmospheric
concentration of the element that can be reliably distinguished from the filter's contribution by multiplying
the standard deviation for the filter batch by 3.3 and dividing by the average volume of air sampled, usually
1700 m3. The resulting value will be the discrimination limit for that element.
12.2 Metal Concentration in Filter
12.2.1 Calculate the air volume sampled, corrected to EPA-reference conditions:
Vstd = Vs
where:
Vstd = volume of ambient air sampled at EPA-reference conditions, m3.
Vs = volume of ambient air pulled through the sampler, m3.
Tstd = absolute EPA-reference temperature, 298°K.
Tm = average ambient temperature, °K.
Pbar = barometric pressure during sampling measurement condition, mmHg.
Pstd = EPA-reference barometric pressure, 760 mmHg.
12.2.2 Metal concentration in the air sample can then be calculated as follows:
C = [(p.g metal/mL)(final extraction volume (i.e., 20 mL)/strip)(9) - Fm]/Vstd
where:
C = concentration, p.g metal/std. m3
p.g metal/mL = metal concentration determined from Section 11.5.
Final extraction volume, mL/strip = total sample extraction volume, mL, from extraction procedure (i.e.
20 mL).
9 = Useable filter area [20 cm x 23 cm (8" x 9")1
Exposed area of one strip [2.5 cm x 20 cm (1" x 8")]
Fm = average concentration of blank filters, p.g.
Vstd = standard air volume pulled through filter, std m3, (25°C and 760 mmHg).
13. Quality Assurance (QA)
13.1 Instrumental Tuning and Standardization
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Method IO-3.4 Chapter IO-3
ICP Methodology Chemical Analysis
13.1.1 The instrument must be tuned by the manufacturer at installation. However, the element lines
should be checked periodically to determine if they have maintained their positions relative to the mercury
profile line. Follow the manufacturer's instructions.
13.1.2 The Thermo Jarrell Ash Company published directions for performing instrument diagnostic
checks and pertinent acceptable data limits (Ward, 1978, 1979 a, b, 1980 a, b). Diagnostic checks should
be run periodically at a frequency dictated by the "goodness" of instrumental QC checks.
13.2 Calibration For Quantitative Analysis
See Section 13.3.2.1.
13.3 Daily QA Check and Analytical Run Sequence
Data validation steps described in this section are primarily instrumental and do not guarantee extraction
efficiency.
13.3.1 Real-Time Judgments: Standards, Gains, Offsets. This system requires virtually no data
computations by the operator. However, the operator is required at several points to judge, based on
historical experience, the validity of numbers generated and to decide whether to continue or stop. During
the standardization, the operator must observe element response to determine if values are normal. The
operator must watch for computer-generated messages reporting gains or offsets that exceed the tolerance
limits. Proper corrective action is based on operator experience and is discussed in Section 14.5.
13.3.2 General Quality Control. The required general quality control requirements for ICP analysis
are discussed below and summarized in Table 6.
13.3.2.1 Initial Calibration. At least two calibration standards and a calibration blank are analyzed at
the beginning of an analysis run. The standards used to calibration are diluted from certified stock standards
(see Section 11.1) and are used within the expiration dates. The calibration standards and blanks are prepared
in the same nitric and hydrochloric acid matrix as the samples.
13.3.2.2 Initial Calibration Verification (ICV). The ICV standards are analyzed immediately following
initial calibration. The ICV standards are prepared from certified stocks having a different manufacturer than
the calibration standards. The measured concentration should be within 90% to 110% of the actual
concentration.
13.3.2.3 Initial Calibration Blank (ICB). The ICB is analyzed immediately following ICV and prior to
the high standard verification. The acceptance criteria for the ICB is the same as for continuing calibration
blank (CCB) verification.
13.3.2.4 High Standard Verification (HSV). Immediately after the analysis of the ICB, and prior to the
analysis of samples, the HSVs are reanalyzed. The measured concentration should be within 95% to 105%
of actual concentration.
13.3.2.5 Interference Check Standards (ICSs). The ICSs are analyzed at the beginning and end of the
run and for every 8 hours of continuous operation. The results for the analytes should be within 80% and
120% of the actual concentration. Samples containing levels of interferences above the levels in the ICS
should be considered for dilution.
13.3.2.6 Continuing Calibration Verification (CCV). CCV standards are prepared from the calibration
standard stocks at the midpoint of the calibration curve. The CCV standards are analyzed at the beginning
of the run prior to samples, after every 10 samples, and at the end of the run prior to the last continuing
calibration blank (CCB) analysis. The measured concentration should be within 90% and 110% of the actual
concentration.
13.3.2.7 Continuing Calibration Blanks (CCBs). The CCBs are analyzed following each CCV. The
results of the CCBs are evaluated as follows:
- The CCBs are compared to the method detection limits.
- The absolute value of the instrument response must be less than the method detection limits.-
Page 3.4-14 Compendium of Methods for Inorganic Air Pollutants June 1999
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Chapter IO-3 Method IO-3.4
Chemical Analysis ICP Methodology
- If not, then sample results for analytes < 5 times the amount in the blank must be flagged or analysis
must be repeated.
13.3.2.8 Reagent Blank (RB). A RB sample is prepared and analyzed with each sample batch. This
analysis is used to determine if concentrations reflect background levels from sample digestion. If the
instrument measured response is greater than the method detection limits, then the sample results for the
affected analyte(s) must be flagged. Samples may be considered candidates for redigestion and reanalysis
for that analyte.
13.3.2.9 Laboratory Control Spike (LCS). An LCS is prepared and analyzed with each sample batch
(or 1 per 20 samples). The results for the analytes should be within 80% to 120% of actual concentration.
If the results are not within this criterion, then strips of the LCS and all samples should be redigested and
reanalyzed.
13.3.2.10 Matrix Spike (MS). A MS sample is prepared and analyzed with each sample batch (or 1 per
20 samples). These samples are used to provide information about the effect of the sample matrix on the
digestion and measurement methodology. The spike is added before the digestion, (i.e., prior to the addition
of other reagents). The percent recovery for the analyte as part of the MS should be between 75% and 125%
for all analytes.
13.3.2.11 Duplicate and/or Spike Duplicate. Duplicate samples and/or matrix spike duplicates are
prepared and analyzed with each sample batch. These samples are used to estimate method precision,
expressed as relative percent difference (RPD). The RPD between the duplicate and/or matrix spike duplicate
final concentrations should be < 20%.
13.3.2.12 Serial Dilution. The ICP serial dilution analysis must be performed on one sample per batch.
After a fivefold serial dilution, the analyte concentration must be within 90% and 110% of the undiluted
sample results.
13.3.2.13 Sample Dilution. Dilute and reanalyze samples that are more concentrated than the linear
calibration limit.
13.4 Corrective Actions
13.4.1 The plasma must operate in a stable mode with a uniform sample feed rate. Failure to reproduce
standards' responses or QC values usually is caused by a partially or totally plugged nebulizer. This
condition may be verified by observing a decrease in the pump rate or the absence of a fog in the nebulizer
spray chamber. A similar effect will be observed if the argon supply pressure or the RF power should
change. Experience with the sample pump and the RF power supply has been excellent, and both appear to
be very stable electronically.
13.4.2 Intermittent failure of QC solutions to fall within the tolerance band may be due to an intermittent
failure in a spectrometer circuit or to a broken nebulizer needle. Both are difficult to detect without extensive
testing or dismantling of equipment. Leaks in the argon supply lines are also likely causes of such problems.
Leaks in the ground-glass joints of the torch-spray chamber can be eliminated by the light use of a good grade
stopcock grease (not silicone-base) (see Section 13.5).
13.4.3 One intended purpose of the repeated analysis of QC solutions was to detect and correct
instrument drift occurring within any 1 day. Experience has shown that drift is not a problem when the
instrument is standardized twice daily. When drift has been detected, it has been attributed to thermal drift
and corrected by repro filing (i.e., adjusting the optical alignment). The instrument must be restandardized
after profiling.
13.4.4 Long-term drift is more difficult to detect. A gradual increase in the gains of short-wavelength
elements over a period of weeks or months is probably due to degradation of mirror coatings. Washing the
mirrors may help in the short term, but usually they must be replaced. Mirrors may be ruined if washed
June 1999 Compendium of Methods for Inorganic Air Pollutants Page 3.4-15
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Method IO-3.4 Chapter IO-3
ICP Methodology Chemical Analysis
improperly; manufacturer-approved procedures should be followed. Gradual degradation of electronic
circuits will also cause long-term drift.
13.5 Routine Maintenance
13.5.1 The torch and spray chambers occasionally must be cleaned. Frequency of cleaning must be
determined through experience, as a schedule and criteria have not been established. Ultrasonic the chambers
in a hot detergent for at least 30 min, soak in aqua regia overnight, and rinse in deionized, distilled water.
[Note: Aqua regia is a strong oxidizing agent. Wear protective clothing and a face shield.]
13.5.2 The ground-glass joints of the torch-spray chamber should be greased with a good grade of
non-silicone base stopcock grease. After reassembly, the torch must be optimized for maximum flux
throughput according to manufacturer's instructions.
13.5.3 Should the plasma be extinguished during an analysis session, the session must be ended.
Restandardization is necessary after the plasma is reignited. Restandardization must be delayed until the
reflected power has been at a minimum for approximately 10 min.
14. Method Safety
The toxicity or carcinogenicity of each reagent used in this method has not been defined precisely; however,
each chemical compound should be treated as a potential health hazard. The laboratory is responsible for
maintaining a current awareness file of OSHA regulations regarding the safe handling of the chemicals
specified in this method. A reference file of material handling data sheets should be made available to all
personnel involved in the chemical analysis.
15. References
1. "Standard Operating Procedures for the ICP-DES Determination of Trace Elements in Suspended
Particulate Matter Collected on Glass-Fiber Filters," EMSL/RTP-SOP-EMO-002, Revision, October,
1983.
2. "Reference Method for the Determination of Suspended Particulates in the Atmosphere (High Volume
Method)," Code of Federal Regulations, Title 40, Part 50, Appendix B, pp. 12-16 (July 1, 1975).
3. "Reference Method for the Determination of Lead in Suspended Particulate Matter Collected from
Ambient Air.," Federal Register 43 (194): 46262-3, 1978.
4. Rhodes, R. C., 1981, "Special Extractability Study of Whatman and Schleicher and Schuell Hi-Vol
Filters," Memo to file, August5, 1981, Quality Assurance Division, Environmental Monitoring Systems
Laboratory, U. S. Environmental Protection Agency, Research Triangle Park, NC.
5. Ward, A. F., The Jarrell-Ash Plasma Newsletter, Volumes I, II, and III.
6. Nygaard, D., and Sot, J. J., "Determination Near the Detection Limit: A Comparison of Sequential and
Simultaneous Plasma Emission Spectrometers," Spectroscopy, Vol. 3(4).
Page 3.4-16 Compendium of Methods for Inorganic Air Pollutants June 1999
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Chapter IO-3 Method IO-3.4
Chemical Analysis ICP Methodology
7. "Simplex Optimization of Multielement Ultrasonic Extraction of Atmospheric Particulates," Harper, et.
al., Analytical Chemistry, Vol. 55(9), August 1983.
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Method IO-3.4
ICP Methodology
Chapter IO-3
Chemical Analysis
TABLE 1. TYPICAL CONCENTRATIONS OF THE MOST CONCENTRATED
WORKING STANDARD,1 TYPICAL ICP CALIBRATING SENSITIVITIES
AND TYPICAL METHOD DETECTION LIMITS2
Element
Al
As
Au
B
Ba
Be
Bi
Ca
Cd
Ce
Co
Cr
Cu
Fe
Ge
Hg
In
K
La
Li
Mg
Mn
Mo
Na
Nb
Ni
P
Pb
Pd
Pt
Re
Rh
Ru
Sb
Se
Si
Sm
Sn
Sr
Ta
Te
Ti
Tl
V
W
Y
Zn
Zr
Most Cone. Working
Std., mg/L
50.0
5.0
5.0
10.0
10.0
2.0
10.0
40.0
4.0
5.0
5.0
4.0
20.0
50.0
5.0
5.0
5.0
20.0
2.0
2.0
40.0
10.0
5.0
80.0
2.0
5.0
20.0
25.0
5.0
5.0
10.0
5.0
10.0
5.0
5.0
50.0
5.0
5.0
5.0
5.0
5.0
5.0
5.0
5.0
5.0
5.0
20.0
5.0
Calibrating Sensitivity,
counts/ug metal
4,887
5,063
11,683
42,892
13,430
57,457
467
52,787
37,438
13,859
2,787
76,772
159,213
16,985
1,645
9,031
520
253
44,468
12,500
70,951
108,751
5,266
186
59,859
4,306
2,941
10,324
7,996
847
288
32,421
5,227
4,246
930
9,152
52,532
469
55,091
21,030
4,676
58,777
3,063
107,250
1,170
35,800
478
18,010
Detection3
Limit
mg/L
0.061
0.025
0.009
0.030
0.003
0.002
1.030
0.103
0.005
0.048
0.015
0.012
0.010
0.034
0.079
0.055
0.081
0.205
0.007
0.003
0.024
0.004
0.009
inoperative
0.11
0.014
0.104
0.032
0.130
0.107
0.150
2.000
0.187
0.025
0.156
0.172
0.024
0.042
0.001
0.145
0.021
0.003
0.152
0.007
0.057
0.004
0.120
0.008
ng/m3
13.5
5.5
1.9
6.6
0.7
0.4
226.6
22.7
1.1
10.6
3.3
2.6
2.2
7.5
17.5
12.1
18.5
45.1
1.5
0.7
5.3
0.9
1.9
inoperative
2.4
3.1
22.9
7.0
7.0
23.5
33.0
440.0
41.1
5.5
34.3
37.8
5.4
9.2
0.2
52.1
4.6
0.7
33.4
1.5
12.5
0.9
26.4
1.8
'The least concentrated working standard contains no metals.
2Data source is 48 determinations of standard No. 1 made from 01/26/83-03/22/83 during analysis of 1982 NAMS filters.
3Based upon sampling rate of 1.13 m3/min for 24-hr for a total sample volume of 1627.2 m3; factor of 9 for partial filter analysis; digestion
of 0.020 L/filter.
Page 3.4-18
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June 1999
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Chapter IO-3
Chemical Analysis
Method IO-3.4
ICP Methodology
TABLE 2. RECOVERIES FROM SPIKED STRIPS1 AND FROM NIST SRM 1648
Element
Spiked Strips1
As
Co
Cu
Fe
Mn
Ni
Pb
Sr
V
Zn
NIST SRM 1648
Ba
Be
Cd
Cu
Fe
Mn
Mo
Ni
Pb
V
Zn
% Recovery
96.5
95.5
76.1
98.3
96.9
96.4
99.1
96.4
94.0
89.4
80
not listed by NIST
114
100
68
88
not listed by NIST
90
95
79
97
%RSD
2.7
3.4
4.3
3.7
4.0
3.9
1.9
4.4
2.1
6.2
0.8
8.5
1.4
1.4
1.6
9.0
1.1
1.9
3.8
'Recovery values based on X-ray fluorescence analytical values taken as "true".
June 1999
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Page 3.4-19
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Method IO-3.4
ICP Methodology
Chapter IO-3
Chemical Analysis
TABLE 3. TYPICAL PRECISION, BIAS, AND CORRELATION COEFFICIENTS
OBTAINED BY SAMPLE/REPLICATE PAIR ANALYSIS1
Element
B
Ba
Cd
Cu
Fe
Mn
Ni
Pb
Sb
Sr
V
Zn
Pairs Found
32
32
17
32
32
32
14
31
4
32
25
31
Coefficient
Variation (%)
10
9
11
4
8
21
10
3
5
7
6
16
Coefficient
Bias (%)
1.0
0
0
-1.0
1.0
5.0
-2.0
0.0
3.0
1.0
-1.0
-3.0
Coefficient
0.95
1.0
1.0
1.0
0.99
0.99
1.0
1.0
0.99
1.0
1.0
0.94
'Based on the analysis of 32 sample/replicate pairs of 1982 NAMS filters from 01/26/83 - 03/22/83. Because these
data were obtained from real samples, there was no control over the actual concentrations. Elements displaying
a large coefficient of variation tended to have mean concentrations in the lower end of the quantifiable range.
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Chapter IO-3
Chemical Analysis
Method IO-3.4
ICP Methodology
TABLE 4. ICP SPECTROMETER ELEMENTS WITH WAVELENGTHS
Element
Al
As
Au
B
Ba
Be
Bi
Ca
Cd
Ce
Co
Cr
Cu
Fe
Ge
Hg
In
K
La
Li
Mg
Mn
Mo
Na
Wavelength
308.22
193.76
242.80
249.77
493.41
313.04
195.33
396.85
226.50
446.02
228.62
357.87
324.75
259.94
199.82
253.65
230.69
766.49
379.48
670.78
279.55
257.61
202.03
589.00
Element
Nb
Ni
P
Pb
Pd
Pt
Re
Rh
Ru
Sb
Se
Si
Sm
Sn
Sr
Ta
Te
Ti
Tl
V
W
Y
Zn
Zr
Wavelength
316.34
231.60
214.91
220.35
363.47
265.95
209.24
343.49
297.66
206.84
196.09
288.16
442.43
189.99
407.77
240.06
214.28
334.90
351.92
292.40
202.99
371.03
206.19
339.20
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Page 3.4-21
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Method IO-3.4
ICP Methodology
Chapter IO-3
Chemical Analysis
TABLE 5. CORRECTION FACTORS FOR SPECTRAL INTERFERENCES
Affecting
Element
Ta
Ta
Al
Al
B
Be
Be
Ce
Hg
Hg
La
La
Pb
Pd
Pd
Pd
Pt
Pt
Pt
Pt
Si
Si
Si
Te
Tl
Tl
Zn
As
As
As
Bi
Bi
Bi
Bi
Bi
Bi
Affecting
Factor
0.0166
0.0026
0.0141
0.0375
0.0181
0.0020
0.0025
0.2313
0.0574
0.0151
0.0028
0.0122
0.1104
0.0247
0.1649
0.0125
0.0600
0.0175
0.1300
0.0210
0.0281
0.1300
0.2495
0.0254
0.0607
0.0229
0.0132
0.0119
0.1736
0.0125
0.0083
0.0212
0.0065
0.0326
0.0155
0.0312
Affected
Element
Co
Fe
Ta
V
Zr
Nb
V
V
Co
Fe
Fe
V
Nb
Nb
Sm
Ti
Cr
Nb
Ta
V
Nb
Ta
Zr
V
Ce
Zr
Ta
Al
Pt
V
Al
Cr
Fe
La
Mg
Mn
Affecting
Element
Bi
Bi
Bi
Bi
Ge
Ge
Ge
Ge
Ge
P
P
P
P
P
P
P
Re
Re
Re
Re
Re
Re
Re
Ru
Ru
Ru
Ru
Ru
Ru
Ru
Ru
W
W
W
As
Affecting
Factor
0.0268
0.0116
0.0041
0.0125
0.0071
0.0015
0.0085
0.0293
0.1489
0.0017
0.0265
0.0016
0.0032
0.0100
0.0017
0.0010
0.0240
0.0110
0.1609
1.2400
0.0556
0.0044
0.2146
0.0141
0.0843
0.0233
0.0827
0.2531
0.0364
5.5170
0.4996
0.0021
0.0039
0.0027
0.0218
Affected
Element
Rh
Se
Si
Sr
Al
Be
Mo
Nb
Ta
Al
Cu
Fe
Mg
Nb
Si
Zn
Al
B
Mn
Mo
Pd
Si
V
Fe
Mn
Mo
Nb
Ta
Ti
V
Zr
Al
Mg
Zn
Ge
Page 3.4-22
Compendium of Methods for Inorganic Air Pollutants
June 1999
-------
Chapter IO-3
Chemical Analysis
Method IO-3.4
ICP Methodology
TART.F. 6 F.XAMPT.F. RF.DTTTRF.D DUALITY CONTROL RFOT JTRFMFNTS FOR TCP ANALYSTS
QC procedure
Initial calibration (1C)
Initial calibration verification
(ICV)
Initial calibration blank (ICB)
High standard verification (HSV
Interference check standard
(ICS)
Continuing calibration
verification (CCV)
Continuing calibration blanks
(CCBs)
Reagent blank (RB)
Laboratory control spike (LCS)
Duplicate and/or spike duplicate
Matrix spike (MS)
Serial dilution
Sample dilution
Typical frequency
At the beginning of the analysis
Immediately after initial
calibrations
Immediately after initial
calibration verification
Following the initial calibration
blank analysis
Following the high standard
verification, every 8 hours, and
at the end of a run
Analyzed before the first sample,
after every 10 samples, and at
the end of the run
Analyzed following each
continuing calibration verification
1 per 40 samples, a minimum of
1 per batch
1 per 20 samples, a minimum of
1 per batch
1 per sample batch
1 per 20 samples per sample
batch
1 per sample batch
Dilute sample beneath the upper
calibration limit and at least 5X
theMDL
Criteria
None
90- 110% of the actual
concentration
Must be less than project
detection limits
95 -105% of the actual
concentration
80- 120% of the actual
concentration
90- 110% of the actual
concentration
Must be less than project
detection limits (MDLs)
Must be less than project
detection limits
80-120% recovery, with the
exception of Ag and Sb
RPD < 20%
Percent recovery of 75-125%
90-110% of undiluted sample
As needed
June 1999
Compendium of Methods for Inorganic Air Pollutants
Page 3.4-23
-------
Method IO-3.4
ICP Methodology
Chapter IO-3
Chemical Analysis
Emission
zone
Lens
Spectrometer
and
readout
induction coil
Torch
Figure 1. Schematic diagram of a typical inductively coupled plasma-optical emission
spectroscopy instrument featuring parts of the instrument most important to the user.
Page 3.4-24
Compendium of Methods for Inorganic Air Pollutants
June 1999
-------
Chapter IO-3
Chemical Analysis
Method IO-3.4
ICP Methodology
Computer
controlled
scanning
monoehromator
Taliflama
Sample pluins
Data out
Figure 2. Simultaneous or sequential multi-element determination of trace elements by ICP.
June 1999
Compendium of Methods for Inorganic Air Pollutants
Page 3.4-25
-------
Method IO-3.4 Chapter IO-3
ICP Methodology Chemical Analysis
[This page intentionally left blank.]
Page 3.4-26 Compendium of Methods for Inorganic Air Pollutants June 1999
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