600485025
DETERMINATION OF DIPHENYLAMINE IN INDUSTRIAL
AND MUNICIPAL WASTEWATERS
J.S. Warner, T.M. Engel and P.J. Mondron
Battelle Columbus Laboratories
Columbus, Ohio 43201
Contract No. 68-03-2956
Project Officer
Thomas Pre ssle y
Physical and Chemical Methods Branch
Environmental Monitoring and Support Laboratory
Cincinnati, Ohio 45263
ENVIRONMENTAL MONITORING AND SUPPORT LABORATORY
OFFICE OF RESEARCH AND DEVELOPMENT
U.S. ENVIRONMENTAL PROTECTION AGENCY
CINCINNATI, OHIO 45268
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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 Contract 68-03-2956
to Battelle Columbus Laboratories. It has been subject to the Agency's
peer and administrative review, and it has been approved for publication
as an EPA document.
ii
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FOREWORD
Environmental measurements are required to determine the quality of
ambient waters and the character of waste effluents. The Environmental
Monitoring and Support Laboratory - Cincinnati, conducts research to:
o Develop and evaluate methods to measure the presence and
concentration of physical, chemical, and radiological pollutants in
water, wastewater, bottom sediments, and solid wastes.
o Investigate methods for the concentration, recovery, and
identification of viruses, bacteria and other microbiological
organisms in water; and, to determine the responses of aquatic
organisms to water quality.
o Develop and operate an Agency-wide quality assurance program to
assure standardization and quality control of systems for monitoring
water and wastewater.
o Develop and operate a computerized system for instrument automation
leading to improved data collection, analysis, and quality control.
This report is one of a series that investigates the analytical behavior
of selected pesticides and suggests a suitable test procedure for their
measurement in wastewater. The method was modeled after existing EPA
methods being specific yet as simplified as possible.
Robert L. Booth, Acting Director
Environmental Monitoring and Support
Laboratory - Cincinnati
111
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ABSTRACT
A method was developed for the determination of diphenylamine in
wastewaters. The method development program consisted of a literature
review; determination of extraction efficiency for each compound from water
using methylene chloride; development of a deactivated silica gel cleanup
procedure; and determination of suitable gas chromatographic (GC) analysis
conditions.
The final method was aplied to Columbus Publicly Owned Treatment Works
(POTW) secondary effluent in order to determine the precision and accuracy
of the method. The wastewater was spiked with diphenylamine at levels of
5 ug/L and 50 ug/1*. Recovery for diphenylamine at the 5 ug/L level was
120 ± 25 percent. Recovery at the 50 yg/L level was 89 ± 11 percent. The
method detection limit (MDL) for diphenylamine in distilled water was
1.6 yg/L (7). In wastewaters it may be higher due to interfering
compounds.
This report was submitted in partial fulfillment of contract No.
68-03-2956 by Battelle Columbus Laboratories under the sponsorship of the
U.S. Environmental Protection Agency. This, report covers the period from
February 1, 1982 to April 30, 1983.
IV
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CONTENTS
Foreword ............................. ill
Abstract ............................. iv
Figures ............................. vi
1. Introduction ...................... 1
2. Conclusions ....................... 2
Extraction and Concentration ............ 2
Cleanup ...................... 2
Chroma tography. .... .............. 2
Validation Studies. ... ............. 2
3. Experimental ...................... 3
Extraction and Concentration ............ 3
Cleanup ...................... 3
Chroma tography ................... 4
Validation Studies ................. 4
4. Results and Discussion ................. 5
Extraction and Concentration ............ 5
Cleanup . . .................... 5
Chroma tography ......... . ......... 5
Validation Studies ................. 8
References ........................ .... 10
Appendix
A. Diphenylamine Method 620
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FIGURES
Number Page
1 GC-AFD Chromatogram of 100 ng of Diphenylamine
(Column 1) 6
. 2 GC-FID Chromatogram of 200 ng of Diphenylamine _
(Column 2) " '
3 Analytical Curve for Diphenylamine 9
vi
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SECTION 1
INTRODUCTION
Diphenylamine(I) is used as a stabilizer in smokeless powders (1,2)
as well as to 'control superficial scald in some varieties of pears and
apples (3,4).
oo
I
The CAS registry number for diphenylamine is 122-39-4 and its IUPAC name
is N-phenylbenzeneamine. It has a melting point of 53-54°C, a boiling
point of 302°C, and an oral LD50 in rats of 300-1000 mg/kg. Common
synonyms for diphenylamine include "Anilinobenzene", "DFA", and "DPA". A
literature review described extractions of diphenylamine from water with
methylene chloride (5) and a cleanup procedure using Bio-Beads S,-X2(6).
Several columns were used for determination of diphenylamine by GC
including 32 SP-1000 (5), 152 UC W-98 and 32 OV-17(2), 32 OV-17 with 0.022
Epikote 1001(4), and 102 OV-101, 62 OV-17, and 52 07-225(6). Detectors
used for GC analyses included a Hall detector (6), a rubidium bead alkali
flame detector (AFD) (4,6), and a mass spectrometer (MS) (2,5).
Electron-impact (El) and chemical-ionization (CI) mass spectra were also
reported (1,2).
Diphenylamine is stable in water at neutral pH, can be extracted from
water with methylene chloride, and contains nitrogen. For these reasons,
the selected approach to the determination of diphenylamine in water
included extraction from water using continuous extraction with methylene
chloride, cleanup using silica gel chromatography, and analysis using
packed column GC-AFD. Standard concentration techniques using
Kuderna-Danish (K-D) equipment were used. The final method is included in
Appendix A of this report.
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SECTION 2
CONCLUSIONS
EXTRACTION AND CONCENTRATION
Diphenylamine can be extracted from water using methylene chloride
with greater than 90 percent recovery by means of continuous extraction
techniques. Use of K-D concentration equipment to perform extract
concentrations did not significantly affect compound recoveries.
CLEANUP
Diphenylamine elutes from deactivated silica gel in six percent ethyl
ether in petroleum ether with greater than 90 percent recovery. This use
of deactivated silica gel was an effective cleanup procedure for extracts
from a columbus POTW secondary effluent, but was not assess for extracts
from any relevant wastewater samples.
CHROMATOGRAPHY
Two packed GC columns, 3Z SP-2250 and 32 SP-1000, were found to be
acceptable for the GC-AFD analysis of diphenylamine. The 3% SP-2250 gave
better peak shape and was used as the primary column. The 32 SP-1000
column was designated as the alternate column.
VALIDATION STUDIES
Recoveries of diphenylamine from distilled water in the 10 to
1000 ug/L concentration range were greater than 85 percent. Analytical
curves constructed from this data were linear. The MDL in distilled water
was 1.6 yg/L. Recoveries of diphenylamine from Columbus secondary POTW
effluent at the 5 and 50 ug/L levels were 120 ± 25 percent and 89 ± 11
percent, respectively.
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SECTION 3
EXPERIMENTAL
Studies were performed to determine if extractions with separator/
funnel and continuous extractors, cleanup by silica gel adsorption
chromatography, concentration using K-D equipment, and analysis using
packed column GC-AFD would be applicable techniques for the determination
of diphenylamine in water. Since recovery data and literature references
indicated that diphenylamine is relatively stable in water, stability
studies were not performed.
EXTRACTION AND CONCENTRATION
*
Extraction of diphenylamine from water was studied using both
separatory funnel and continuous extraction techniques. In both cases one
liter of distilled water was used. The sample was adjusted to pH 7 by
addition of 6N sodium hydroxide or 6N sulfuric acid. For the
separatory funnel studies, the distilled water was spiked with
diphenylamine at the 5, 10, 50, 100, 500, and 1000 ug/L level and
extracted three times with 60 mL. each of methylene chloride. For the
continuous extractor studies the water was spiked at the 10 and 100 ug/L
levels.and extracted with methylene chloride overnight. These studies
were done in duplicate. The extracts were dried by passing them through
10 cm of anhydrous granular sodium sulfate, concentrated to one mL and
analyzed by GC-AFD.
CLEANUP
•
Activated silica gel, 20 grams, was stirred with 100 mL of acetone
and 1.2 mL of reagent water for 30 minutes. The slurry was transferred to
a chromatographic column, and the solvent was allowed to elute and
discarded. The column, was then sequentially washed with 20 aL of
methylene chloride and 30 mL of petroleum ether. Petroleum ether, 50 mL,
was suspended over the silica gel. Amounts of either 10 or 100 ug
diphenylamine dissolved in 5 mL of methylene chloride was added to the
above mentioned petroleum ether. This solvent plus an additional 50 mL of
petroleum ether were eluted from the column and collected (Fl). Nine
additional 25-mL solvent elutions were collected: six percent ethyl ether
in petroleum ether (F2); 15 percent ethyl ether in petroleum ether (F3);
50 percent ethyl ether in petroleum ether (F4); ethyl ether (F5); six
percent acetone in ethyl ether (F6); 15 Percent acetone in ethyl ether
(F7); 50 percent acetone in ethyl ether (F8); acetone (F9); and six
percent methanol in acetone (F10). Each fraction was concentrated to
approximately 4 mL after addition of 2.5 mL of toluene. The fractions
were then transferred to 5-mL volumetric flasks and diluted to volume with
toluene.
3
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CHROMATOGRAPHY
Two columns were evaluated for the determination of diphenylamine, 32
SP-2250 on 100/120 mesh Supelcoport and 3Z SP-1000 on 100/120 mesh
Supelcoport. The 3Z SP-2250 column has a maximum temperature limit of
300°C. The 32 SP-1000 column has a maximum temperature limit of only 250°
C.
VALIDATION STUDIES
The HDL for diphenylamine was determined by analyzing seven replicate
distilled water samples spiked at the 5 ug/L concentration level (7). The
sample extracts were cleaned up using the silica gel cleanup procedure
prior to analysis. The amounts recovered were determined by external
standard calibration and the MDL was calculated from these data.
Distilled water was also spiked in duplicate at the 10, 50, 100, 500,
and 1000 ug/L concentration levels and recoveries of the diphenylamine was
determined as described earlier. An analytical curve was generated by
plotting the amount spiked into the samples versus the amount recovered
from the samples.
A relevant wastewater was not available for diphenylamine and
Columbus POTW secondary effluent was used for wastewater validation
studies. Seven replicates of the wastewater were analyzed to determine
the background levels. The wastewater was spiked with diphenylamine at
the 5 and 50 ug/L concentration levels, processed and analyzed. Seven
replicate extractions were performed at each concentration level.
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SECTION 4
RESULTS AND DISCUSSION
EXTRACTION AND CONCENTRATION
Data from separatory funnel extractions of diphenylamine from reagent
water indicated that recoveries of diphenylamine were unacceptably low
below the 100 \ig/mL conentration level. Recovery data are given in Table
TABLE 1. RECOVERY OF DIPHENYLAMINE FROM WATER USING SEPARATORY
FUNNEL TECHNIQUES
Amount Spiked, Amount Recovered,
Ug/L ug/L
5 0.4 ± 0.1 (a)
10 2.7 ± 0.3 (b)
50 29 ± 2.6 (b)
100 94 ± 7.7 (b)
500 390 ± 42 (b)
(•a) Average of seven extractions; second figure is relative
standard deviation.
(b) Average of two extractions; second figure is relative range.
Use of continuous extractors improved recoveries of diphenylamine at lower
concentration levels as demonstrated by the recovery data in Table 2.
TABLE 2. RECOVERY OF DIPHEYLAMINE FROM WATER USING CONTINUOUS
EXTRACTION TECHNIQUES
Amount Spiked, Amount Recovered,
Ug/L Ug/L
5
10
50
100
500
1000
3.6 ± 0.5 (a)
8.6 ± 1.2 (b)
49 ± 1.7 (b)
95 ± 1.9 (b)
500 ±11 (b)
950 ± 8.0 (b)
(a) Average of seven extractions; second figure is relative standard
deviation.
(b) Average of two extractions; second figure is relative range.
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Use of continuous extractors as opposed to separator? funnels for
extraction of diphenylamine from water improved recoveries. For this
reason, continuous extractors were used for all diphenylamine method
validation studies.
CLEANUP
Diphenylamine eluted from deactivated silica gel in fraction 3 (six
percent ethyl ether in petroleum ether). Recoveries of 10 and 100 yg of
diphenylamine were 108 and 102 percent, respectively.
CHROMATOGRAPHY
Both the 32 SP-2250 and 3% SP-1000 columns were satisfactory for the
GC determination of diphenylamine. The 32 SP-2250 column, however, gave
slightly better peak shape and was chosen as the primary column. The
following conditions were used for the columns:
Column: 1.8m x 2mm ID 32 SP-2250 on 100/120
mesh Supelaoport or 1.8 m x 2mm ID 3%
SP-1000 on 100/120 mesh Supelcoport
Detector: Alkali flame
Injector Temperature: 280°C
Detector Temperature: 300 °C
Oven Temperature: 80aC for 4 minutes; programmed from
80 °C to 300°C at 8 C/minute; held at
300°C for 4 minutes (SP-2250 column)
80°C for 4 minutes; programmed from
80°C to 250°C at 88C/minute; held.
250°C for 4 minutes (SP-1000 column).
Carrier Gas:. Helium-at 30 mL/minute
Chromatograms obtained under these conditions are shown in Figures 1 and
2.
VALIDATION STUDIES
Recovery of diphenylamine from distilled water at the 5 ug/L level
was 3.6 ± 0.5 ug/L. This figure is an average of seven replicate
analyses. The HDL in distilled water was calculated to be 1.6 ug/L.
Recoveries of diphenylamine from distilled water at the 10, 50, 100, 500,
and 1000 ug/L levels were 8.6 ± 1.2, 49 ± 1.7, 95 ± 1.9, 500 ± 11 and
950 ± 8.0 Pg/L, respectively. These data were the averages of duplicate
analyses. The resultant analytical curve is shown in Figure 3.
Recoveries of diphenylamine from Columbus POTW secondary effluent at
the 5 and 50 ug/L levels were 120 ± 25 percent and 89 ± 11 percent,
respectively. These data were the averages of seven replicate analyses.
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*—i "i"!—r—r~T" ••'*!" t"»—»*t—|—v- T—»—i""f--i—i—r--i—|— i •••-•!-•f
31.8
33.0 33.0
RETENTION TIME, minutes
Figure i. OC-AFD Cliromatogram of 100 ng of Diphenylamine (Column 1),
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00
30.0 31.5
3.3. (
RETENTION TIME, minutes
PlRiire 2. CC-PID Chroma tog ram of 200 IIR of Diphenylamlne (Column 2).
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IStolflZ
loonjo
r /*
900.0-
f
aon.rj"
i '•
700.0.
600.fr
Amount Recovered, j-
Wg/L L
snn.o
r
400.0.
i
!
9
300. (T
200.0
• •'
loo Ji X
\s.\.\.\
UNHJUilll Utef O*l« .IMHi
T OflBDSTi 3>2Z2
3A .28
.1,1,1,1.1,1.1
400.0 SOU) tfO.O TOO-O fULa 100.0
Amount Spiked, ug/L
Figure 3. Analytical Curve for Diphenylamine
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REFERENCES
1. Ala, A. Mass Spectra of Diphenyiamine Compounds with Nirto and
Nitroso Substituents and of Tetraphenylhydrazine. Explosivs to ffe,
17(7):156-164, 1969.
2. Mach, M.H., A. Polios, and P.F. Jones. Feasibility of Gunshot
Residue Detection Via Its Organic Constituents Part I. Analysis
of Smokeless Powders by Combined Gas Chromatography-Cheaiical
lonization Mass Spectrometry. .J. Forensic Sei., 23(3)-433-445,
1978.
3. Luke, B.C., and S.A. Cosseus. Determination of Diphenylamine
Residues in Apples. Bull. Environm. Contam. Toxicol., 24:745-751,
1980.
4. Allen, J.G. and K.J. Hall. Methods for the Determination
of Diphenylamine Residues in Apples. J. Agric Food Chem.,
28(2):255-258, 1980.
5. Jungclaus, G.A. , L.M. Games, and R.A.. Kites. Identification
of Trace Organics Compounds in Tire Manufacturing Plant Wastewatars.
Analytical Chemistry. 48(13):1894-1896, 1976.
6. Diachenko, G.W. Determiation of Several Industrial Aromatic
Amines in Fish. Environmental Science and Technology,
13(3):329-333, 1979.
*
7. Glaser, J.A., et al. "Trace Analysis for Wastewaters", Environmental
Science and Technology. 15, 1426 (1981).
10
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METHOD 620 DETERMINATION OF DIPHENYLAMINE IN
MUNICIPAL AND INDUSTRIAL WASTEWATERS
BY GAS CHROMATOGRAPHY
1. Scope and Application
1.1 This method covers the determination of diphenylamine CAS No.
122-39-4.
1.2 This is a gas chromatographic (GC) method applicable to the
determination of diphenylamine in municipal and industrial
discharges.
1.3 The method detection limit (MDL, defined in Section.15)
for diphenylamine is listed in Table 1. The MDL for a specific
wastewater may differ from those listed, depending upon the
nature of interferences in the sample matrix.
1.4 The sample extraction and concentration steps in this method
are similar to those of other 600 series methods. Thus, a single
sample may be extracted to measure the compounds included in the
scope of the methods. When cleanup is required, the concentration
levels must be high enough to permit selecting aliquots, as
necessary, in order to apply appropriate cleanup procedures.
1.5 This method is restrictedto use by or under the supervision of
analysts experienced in the use of gas chromatography and in the
interpretation of gas chromatograms. Each analyst must demonstrate
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the ability to generate acceptable results with this method using
the procedure described in Section 8.2.
1.6 When this method is used to analyze unfamiliar samples for^any or
all of the compounds above, compound identifications should be sup-
ported by at least one additional qualitative technique. This
method describes analytical conditions for a second gas chrcmato-
graphic column that can be used to confirm measurements made with
the primary column. Section 14 provides gas chromatograph/mass
spectrometer (QC-MS) criteria appropriate for the qualitative con-
firmation of compound identifications.
2. Summary of Method
2.1 ' A measured volume of sample, approximately 1 liter, is solvent
extracted with methylene chloride using a continuous extractor.
The methylene chloride extract is dried and concentrated to 5.0 ml.
Sas chromatographic conditions are described which permit the sepa-
ration and measurement of the compounds in the extract by alkali
flame detector (AFD) gas chromatography.
2.2 This method provides an optional silica gel column cleanup proce-
dure to aid in the elimination of interferences which may be
encountered.
3. Interferences
3.1 Method interferences may be caused by contaminants in solvents,
reagents, glassware, and other sample processing apparatus that
lead to discrete artifacts or elevated baselines in gas chro-
matograms. All reagents and apparatus must be routinely demon-
strated to be free from interferences under the conditions of the
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analysis by running laboratory reagent blanks as described in
Section 8.5.
n
3.1.1 Glassware must be scrupulously cleaned. Clean all glass-
ware as soon as possible after use by thoroughly rinsing
with the last solvent used in it. Follow by washing with
hot water and detergent and thorough rinsing with tap and
reagent water. Drain dry, and heat in an oven or muffle
furnace at 400*0 for 15 to 30 min. Thermally stable
materials such as PCBs miqht not be eliminated by this treatment
Thorough rinsing with acetone and pesticide quality hexane
may be substituted for the heating. After drying and cool-
ing, seal and store glassware in a clean environment to
prevent any accumulation of dust or other contaminants.
Store inverted or capped with aluminum foil.
3.1.2 The use of high purity reagents and solvents helps to mini-
•
raize interference problems. Purification of solvents by
distillation in all-glass systems may be required.
3.2 Matrix interferences may be caused by contaminants that are coex-
tracted from the sample. The extent of matrix interferences will
i
vary considerably from source to source, depending upon the nature
and diversity of the industrial complex or municipality being
sampled. The cleanup procedure in Section 11 can be used to over-
come many of these interferences, but unique samples may require
additional cleanup approaches to achieve the MDL listed in Table 1.
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4. Safety
4.1 The toxicity of carcinogenicity of each reagent used in this method
has not been precisely defined; however, each chemical compound
should be treated as a potential health hazard. From this view-
point, exposure to these chemicals must be reduced to the lowest
->•
possible level by whatever means available. The laboratory is re-
sponsible for maintaining a current awareness file of OSHA regu-
lations regarding the safe handling of the chemicals specified in
this method. A reference file of material data handling sheets
should also be made available to all personnel involved in the
chemical analysis. Additional references to laboratory safety are
available and have been identified3" for the information of the .
analyst.
5. Apparatus and Materials
5.1 Sampling equipment, for discrete or composite sampling.
5.1.1 Grab sample bottle - Amber borosilicate or flint glass, 1-
liter or 1-quart volume, fitted with screw caps lined with
Teflon. Aluminum foil may be substituted for Teflon if the
sample is not corrosive. If amber bottles are not avail-
able, protect samples from light. The container and cap
liner must be washed, rinsed with acetone or methylene
chloride, and dried before use to minimize contamination.
5.1.2 Automatic sampler (optional) - Must incorporate glass
sample containers for the collection of a minimum of
250 ml. Sample containers must be kept refrigerated at 4°C
and protected from light during compositing. If the
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sampler uses a peristaltic pump, a minimum length of
compressible silicone rubber tubing may be used. Before
use, however, the compressible tubing should be thoroughly
rinsed with methanol, followed by repeated rinsings with
reagent water to minimize the potential for contamination
of the sample. An integrating flow meter is required to
collect flow proportional composites.
5.2 Glassware (All specifications are suggested. Catalog numbers are
included for illustration only.)
5.2.1 Continuous extractor - 2000-mL, available from Paxton Woods
Glass Shop, Cincinnati, Ohio or equivalent.
5.2.2 Drying Column - Chromatographic column 400 mm long x 10 mm
ID.
5.2.3 Chromatographic column - 400 mm -long x 19 mm ID with 250 ml
reservoir at the top and Teflon stopcock (Kontes K-420290
or equivalent).
5.2.4 Concentrator tube, Kuderna-Danish - 25-mL, graduated
(Kontes K-570050-1025 or equivalent). Calibration must be
checked at the volumes employed in the test. A ground
glass stopper is used to prevent evaporation of extracts.
5.2.5 Evaporative flask, Kuderna-Danish - 500-mL (Kontes K-
570001-0500 or equivalent). Attach to concentrator tube
with springs.
5.2.6 Snyder column, Kuderna-Oanish - three-ball macro (Kontes K-
503000-0121 or equivalent).
5.2.7 Snyder column, Kuderna-Oanish - two-ball micro (Kontes K-
569001-0219 or equivalent).
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5.2.8 Vials - Amber glass, 10 to 15 ml capacity with Teflon lined
screw-cap.
5.2.9 Volumetric flask - 5-mL with glass stopper.
5.3 Boiling chips - approximately 10/40 mesh carborundum. Heat to
400°C for 4 hours or extract in a Soxhlet extractor with methylene
chloride.
5.4 Water bath - Heated, capable of temperature control i2°C). The
bath should be used in a hood.
5.5 Balance - Analytical, capable of accurately weighing to the nearest
0.0001 g.
5.6 Gas chromatograph - Analytical system complete with gas chromato-
graph suitable for on-column injection and all required accessories
including syringes, analytical columns, gases, detector, and strip-
chart recorder. A data system is recommended for measuring peak
areas.
•
5.6.1 Column 1 - ISO cm long x 2 mm ID glass, packed with 3%
SP2250 on Supelcoport (100/120 mesh) or equivalent. This
column was used to develop the method performance state-
ments in Section 15. Guidelines for the use of alternate
columns are provided in Section 12.1.
5.6.2 Column 2 - ISO cm long x 2 mm ID glass, packed with 3/J SP-
1000 on Supelcoport (100/120 mesh) or equivalent.
5.6.3 Detector - Alkali-flame detector (AFD), sometimes referred
to as a nitrogen-phosphorous detector (NPD) or a thermionic
specific detector (TSD). This detector has proven effec-
tive in the analysis of wastewaters for the compounds
listed in the scope and was used to develop the method
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performance statements in Section 15. Alternative
detectors, including a mass spectrometer, may be used in
accordance with the provisions described in Section 12.1.
6. Reagents
6.1 Reagent water - Reagent water is defined as a water in which an
interferent is not observed at the method detection limit of each
parameter of interest.
6.2 Methylene chloride, acetone, methanol, petroleum ether, ethyl
ether, toluene-distilled-in-glass quality or equivalent. Ethyl
ether must be free of peroxides as indicated by EM Quant Test
Strips (available from Scientific Products Co., Catalog No.
P1126-8, and other suppliers). Procedures recommended for removal
of peroxides are provided with the test strips.
6.3 Sodium sulfate (ACS) granular, anhydrous; heated in a muffle fur-
nace at 400°C overnight.
6.4 Silica gel - Davison Grade 923, 100-200 mesh; activated by heating
for 24 hours at 150°C.
6.5 ei^Sulfuric Acid - Slowly add 16.7 mL of cone. l^SO/v (94%) to
about 50 mL of reagent water. Dilute to 100 mL with reagent water.
6.6 6N_ Sodium hydroxide - Dissolve 24.0 grams of sodium hydroxide in
100 mL of reagent water.
6.7 Stock standard, solutions (1.00 vg/tiL) - Stock standard solutions
can be prepared from pure standard materials or purchased as certi-
fied solutions.
6.7.1 crepare stock standard solutions by accurately weighing
about 0.0100 grams of pure material. Dissolve the material
in distilled-in-glass quality methanol and-dilute to volume
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in a 10-mL volumetric flask. Larger volumes can be used at
the convenience of the analyst. If compound purity is cer-
tified at 96% or greater, the weight can be used without
correction to calculate the concentration of the stock
standard. Commercially prepared stock standards can be
used at any concentration if they are certified by the man-
ufacturer or by an independent source.
6.7.2 Transfer the stock standard solutions into Teflon-sealed
screw-cap bottles. Store at 4°C and protect from light.
Frequently check stock standard solutions for signs of
degradation or evaporation, especially just prior to pre-
paring calibration standards from them.
6.7.3 Stock standard solutions must be replaced after six months
or sooner if comparison with check standards indicates a
problem.
7. Calibration
7.1 Establish gas chromatographic operating parameters equivalent to
those indicated in Table 1. The gas chromatographic system may be
calibrated using either the external standard technique (Section
7.2) or the internal standard technique (Section 7.3).
7.2 External standard calibration procedure:
7»2.1 For each compound of interest, prepare calibration
standards at a minimum of three concentration levels by
adding volumes of one or more stock' standards to a
volumetric flask and diluting to volume with toluene. One
of the external standards should be at a concentration
near, but above, the method detection limit. The other
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concentrations should correspond to the expected range of
concentrations found in real samples or should define the
working range of the detector.
7.2.2 Using injections of 2 to 5 ul of each calibration standard,
tabulate peak height or area responses against the mass
injected. The results can be used to prepare a calibration
curve for each parameter. Alternatively, the ratio of the
response to the mass injected, defined as the calibration
factor (CF), can be calculated for each compound at each
standard concentration. If the relative standard deviation
of the calibration factor is less than 10% over the working
range, the average calibration factor can be used in place
of a calibration curve.
7.2.3 The working .calibration curve or calibration factor must be
verified on each working shift by the measurement of one or
more calibration standards. If the response for any com-
pound varies from the predicted response by more than +10*,
the test must be repeated using a fresh calibration
standard. Alternatively, a new calibration curve or
calibration factor must be prepared for that parameter.
7.3 Internal standard calibration procedure. To use this approach, the
analyst must select one or more internal standards similar in ana-
lytical behavior to the compounds of interest. The analyst must
further demonstrate that the measurement of the internal standard
is not affected by method or matrix interferences. Due to these
limitations, no internal standard applicable to all samples can be
suggested, although carbazole has been used successfully in some
instances.
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7.3.1 Prepare calibration standards at a minimum of three concen-
tration levels for each parameter of interest by adding
volumes of one or more stock standards to a volumetric
flask. To each calibration standard, add a known constant
amount of one or more internal standards, and dilute to
volume with toluene. One of the standards should be at a
concentration near, but above, the method detection limit.
The other concentrations should correspond to the expected
range of concentrations found in real samples, or should
define the working range of the detector.
7.3.2 Using injections of 2 to 5 ul of each calibration standard,
tabulate the peak height or area responses against the con-
centration for each compound and internal standard. Calcu-
late response factors (RF) for each compound as follows:
RF - (AsCis)/(AiSCs)
where:
As » Response for the compound to be measured.
A-JS * Response for the internal standard.
Cis * Concentration of the internal standard in vq/l.
Cs « Concentration of the compound to be measured
in vg/L.
If the RF value over the working range is constant, less
than 105t relative standard deviation, the RF can be assumed
to be invariant and the average RF can be used for calcula-
tions. Alternatively, the results can be used to plot a
calibration curve of response ratios, As/AjS against RF.
20
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7.3.3 The working calibration curve or RF must be verified on
each working shift by the measurement of one or more cali-
bration standards. If the response for any compound varies
from the predicted response by more than ^10%, the test
must be repeated using a fresh calibration standard.
Alternatively, a new calibration curve must be prepared for
that compound.
7.4 Before using any cleanup procedure, the analyst must process a
series of calibration standards through the procedure to validate
elution patterns and the absence of interferences from the
reagents.
8. Quality Control
8.1 Each.laboratory using this method is required to operate a formal
quality control program. The minimum requirements of this program
consist of an initial demonstration of laboratory capability and
the analysis of spiked samples as a continuing check on
performance. The laboratory is required to maintain performance
records to define the quality of data that is generated.
8.1,1 Before performing any analyses, the analyst must demon-
strate the ability to generate acceptable accuracy and
precision with this method. This ability is established as
described in Section 8.2.
8.1.2 In recognition of the rapid advances occurring in chroma-
tography, the analyst is permited certain options to improve
the separations or lower the cost of measurements. Each
time such modifications tc the method are made, the analyst
is required to repeat the procedure in Section 8.2.
21
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8.1.3 The laboratory must spike and analyze a minimum of 10* of
all samples to monitor continuing laboratory performance.
This procedure is described in Section 8.4.
8.2 To establish the ability to generate acceptable accuracy and preci-
sion, the analyst must perform the following operations.
8.2.1 Select a representative spike concentration for each com-
pound to be measured. Using stock standards, prepare a
quality control check sample concentrate in methanol 1000
times more concentrated than the selected concentrations.
8.2.2 Using a pipet, add 1.00 ml of the check sample concentrate
to each of a minimum of four 1000-mL aliquots of reagent
water. A representative wastewater may be used in place of
the reagent water, but one or more additional aliquots must
be analyzed to determine background levels, and the spike
level must exceed twice the background level for the test
to be valid. Analyze the aliquots according to the method
beginning in Section 10.
8.2.3 Calculate the average percent recovery (R), and the
standard deviation of the percent recovery (s), for the
results. Wastewater background corrections must be made
before R and s calculations are performed.
8.2.4 Using the appropriate data from Table 2, determine the
recovery and single operator precision expected for the
method, and compare these results to the values measured in
Section 8.2.3. If the data are not comparable, the analyst
must review potential problem areas and repeat the test.
22
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8.3 The analyst must calculate method performance criteria and define
the performance of the laboratory for each spike concentration and
parameter being measured.
8.3.1 Calculate upper and lower control limits for method perfor-
mance as follows:
Upper Control Limit (UCL) » R + 3 s
Lower Control Limit (LCL) » R « 3 s
where R and s are calculated as in Section 8.2.3. The UCL
and LCL can be used to construct control charts that are
useful in observing trends in performance.
8.3.2 The laboratory must develop and maintain separate accuracy
statements of laboratory performance for wastewater
samples. An accuracy statement for the method is defined
as R £ s. The accuracy statement should be developed by
the analysis of four aliquots of wastewater as described in
•
Section 8.2.2, followed by the calculation R and s.
Alternately, the analyst must use four wastewater data
points gathered through the requirement for continuing
quality control in Section 8.4. The accuracy statements
should be updated regu-larly.
8.4 The laboratory is required to collect in duplicate a portion of
their samples to monitor spike recoveries. The frequency of spiked
sample analysis must be at least 10% of all samples or one sample
per month, whichever is greater. One aliquot of the sample must be
spiked and analyzed as described in Section 8.2. If the recovery
23
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for a particular compound does not fall within the control limits
for method performance, the results reported for that compound in
all samples processed as part of the same set must be qualified as
described in Section 13.3. The laboratory should monitor the fre-
quency of data so qualified to ensure that it remains at or below
5*.
8.5 Before processing any samples, the analyst should demonstrate
through the analysis of a 1-liter aliquot of reagent water that all
glassware and reagents interferences are under control. Each time
a set of samples is extracted or there is a change in reagents, a
laboratory reagent blank should be processed as a safeguard against
laboratory contamination.
8.6 It is recommended that the laboratory adopt additional quality as-
surance practices for use with this method. The specific practices
that are most productive depend upon the needs of the laboratory
and the nature of the samples. Field duplicates may be analyzed to
monitor the precision of the sampling technique. When doubt exists
over the identification of a peak on the chromatogram, confirmatory
techniques such as gas chromatography with a dissimilar column,
specific element detector, or mass spectrometer must be used.
Whenever possible, the laboratory should perform analysis of
standard reference materials and participate in relevant
performance evaluation studies.
9. Samples Collection, Preservation, and Handling
9.1 Grab samples must be collected in glass containers. Conventional
sampling practices should be followed; however, the bottle must
24
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not be prerinsed with sample before collection. Composite samples
should be collected in refrigerated glass containers in accordance
with the requirements of the program. Automatic sampling equipment
must be as free as possible of plastic and other potential sources
of contamination.
9.2 The samples must be iced or refrigerated at 4°C from the time of
collection until extraction.
9.3 Adjust the pH of the sample to 6 to 8 with 6N. sodium hydroxide or
6N sulfuric acid immediately after sampling.
10. Sample Extraction
10.1 Assemble continuous extraction apparatus by placing 5-10
carborundum chips into the 500-mL round-bottom flask and attaching
to the extraction flask.
10.2 Add 400 ml methylene chloride to the extraction flask. Some
methylene chloride should displace into the round-bottom flask.
10.3 Mark the water meniscus on the side of the sample bottle for later
determination of sample volume. Pour the entire sample into the
extraction flask and add sufficient distilled water to fill the
extraction flask (two liters total volume aqueous phase).
10.4 Check the pH of the sample with wide range pH paper and adjust to 6
to 8 with 6 N sodium hydroxide or 5 N sulfuric acid.
10.5 Connect the stirring apparatus to the extraction flask without the
frit touching the sample. Heat methylene chloride in round-bottom
flask to continuous reflux and continue heating for 30 minutes to
one hour, until frit is thoroughly wetted with methylene chloride.
25
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10.6 Lower frit until it just touches the sample and start the stirring
apparatus rotating.
10.7 Continuously extract sample for 18-24 hours.
10.8 Assemble a Kuderna-Danish (K-D) concentrator by attaching a 10-ml
concentrator tube to a 500-mL evaporative flask. Other concentra-
tion devices or techniques may be used in place of the K-D if the
requirements of Section 8.2 are met.
10.9 Pour the extract from the round-bottom flask through a drying
column containing about 10 cm of anhydrous sodium sulfate, and
collect the extract in the K-D concentrator. Rinse the flask and
column with 20 to 30 ml of methylene chloride to complete the
quantitative transfer. Once the flask rinse has passed through the
drying column, rinse the column with 30 to 40 ml of methylene
chloride.
10.10 Add 1 to 2 clean boiling chips to the evaporative flask and attach
•
a three-ball Snyder column. Prewet the Snyder column by adding
about 1 mL methylene chloride to the top. Place the K-D apparatus
on a hot water bath, 60 to 65°C, so that the concentrator tube is
partially immersed in the hot water, and the entire lower rounded
surface of the flask is bathed with hot vapor. Adjust the vertical
position of the apparatus and the water temperature as required to
complete the concentration in 15 to 20 min. At the proper rate of
distillation, the balls of the column will actively chatter but the
chambers will not flood with condensed solvent. When the apparent
volume of liquid reaches approximately 4 ml, remove the K-0 appara-
tus and allow it to drain and cool for at least 10 min.
26
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10.11 Remove the Snyder column and flask and adjust the volume of the
extract to 5.0 raL with methylene chloride. Stopper the
concentrator tube and store refrigerated if further processing will
not be performed immediately. If the extract is to be stored
longer than two days, transfer the extract to a screw capped vial
with a Teflon-lined cap. If the sample extract requires no further
cleanup, proceed with solvent exchange to toluene and gas chromatographic
analysis as described in sections 11.5 and 12 respectively. If the
sample requires cleanup, proceed to Section 11.
10.12 Determine the original sample volume by refilling the sample bottle
to the mark and transferring the water to a 1000-mL graduated
cylinder. Record the sample volume to the nearest 5 ml.
11. Cleanup and Separation
11.1 Cleanup procedures may not be necessary for a relatively clean
sample matrix. The cleanup procedure recommended in this method
has been used for the analysis of various clean waters and indus-
trial effluents. If particular circumstances demand the use of an
alternative cleanup procedure, the analyst must determine the elu-
tion profile and demonstrate that the recovery of each compound of
interest is no less than 85JJ.
11.2 Stir 20 g of silica gel in 100 mL of acetone and 1.2 ml of reagent
water for 30 minutes on a stirring plate. Transfer the slurry to a
chromatographic column (silica gel may be retained with a plug of
glass wool). Wash the column with 20 mL of methylene chloride and then
with 30 ml of petroleum ether. Use a column flow rate of 2 to 2.5
ml/min throughout the wash and elution profiles. Add an additional
50 ml of petroleum ether to the head of the column.
27-
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11.3 Add the extract from Section 10.11 to the head of the column.
Allow the solvent to elute from the column until the Florisil is
almost exposed to the air. Elute the column with 50 ml of 6% ethyl
ether in petroleum ether. Discard this fraction.
11.4 Elute the column with 100 ml of 15% ethyl ether in petroleum ether
and collect in a KD apparatus.
11.5 Add 2.5 ml of toluene to the fraction. Concentrate the fraction to
approximately 4 mL with the water bath at 75-80°C as described in
Section 10.10. Transfer the sample to a 5-mL volumetric flask and
dilute to 5 mL with toluene. Proceed with gas chromatographic
analysis.
12. Gas Chromatoaraphy
12.1 Table 1 summarizes the recommended operating conditions for the gas
chromatograph. Included in this table are estimated retention
times and method detection limits that can be achieved by this
method. An example of the separations achieved by Column 1 and
Column 2 are shown in Figures 1 and 2. Other packed columns,
chromatographic conditions, or detectors may be used if the
requirements of Section 8.2 are met. Capillary (open-tubular)
columns may also be used if the relative standard deviations of
responses for replicate injections are demonstrated to be less than
6% and the requirements of Section 8.2 are met.
12.2 Calibrate the gas chromatographic system daily as described in
Section 7.
12.3 If an internal standard approach is being used, the analyst must
not add the internal standard to the sample extracts until
immediately before injection into the instrument. Mix thoroughly.
28
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12.4 Inject 2 to 5 nl of the sample extract using the solvent flush
technique.® Record the volume injected to the nearest 0.05-al, and
the resulting peak sizes in area or peak height units.
12.5 The width of the retention time window used to make identifications
should be based upon measurements of actual retention time varia-
tions of standards over the course of a day. Three times the
standard deviation of a retention time for a compound can be used
to calculate a suggested window size; however, the experience of
the analyst should weigh heavily in the interpretation of
chromatograms.
12.6 If the response for the peak exceeds the working range of the
system, dilute the extract and reanalyze.
12.7 If the measurement of the peak response -is prevented by the
presence of interferences, further cleanup is required.
13. Calculations
13.1 Determine the concentration of individual compounds in the sample.
13.1.1 If the external standard calibration procedure is used,
calculate the amount of material injected from the peak
response using the calibration curve or calibration factor
in Section 7.2.2. The concentration in the sample can be
calculated as follows:
Concentration, ag/L »
where:
. 29
-------
A » Amount of material injected in nanograms.
V-f • Volume of extract injected in ul.
Vt * Volume of total extract in ^L.
Vs * Volume of water extracted in mL.
13.1.2 If the internal standard calibration procedure was used,
calculate the concentration in the sample using the
response factor (RF) determined in Section 7.3.2 as
follows:
Concentration, ,g/l *
where:
As » Response for the compound to be measured. ,
A-fs a Response for the internal standard.
Is * Amount of internal standard added to each
extract in */g.
V0 » Volume of water extracted in liters.
13.2 Report results in micrograms per liter without correction for
recovery data. When duplicate and spiked samples are analyzed,
report all data obtained with the sample results.
13.3 For samples processed as part of a set where the laboratory spiked
sample recovery falls outside of the control limits in Section 8.3,
data for the affected compounds must be labeled as suspect.
14. SC-MS Confirmation
14.1 It is recommended that GC-MS techniques be judiciously employed to
support qualitative identifications made with this method. The
mass spectrometer should be capable of scanning the mass range from
30
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35 amu to a mass 50 amu above the molecular weight of the compound.
The instrument must be capable of scanning the mass range at a rate
to produce at least 5 scans per peak but not to exceed 7 seconds
per scan utilizing a 70-V (nominal) electron energy in the electron
impact ionization mode. A GC to MS interface constructed of all-
>
glass or glass-lined materials is recommended. When using a fused
silica capillary column, the column outlet should be threaded
through the interface to within a few mm of the entrance to the
source ionization chamber. A computer system should be interfaced
to the mass spectrometer that allows the continuous acquisition and
storage on machine readable media of all mass spectra obtained
throughout the duration of the chromatographic program.
14.2 Gas chromatographic columns and conditions should be selected for
optimum separation and performance. The conditions selected must
be compatible with standard GC-MS operating practices. Chromato-
graphic tailing factors of less than 5.0 must be achieved. The
calculation of tailing factors is illustrated in Method 625.
14.3 At the beginning of each day that confirmatory analyses are to be
performed, the GC-MS system must be checked to see that all DFTPP
q
performance criteria are achieved.
14.4 To confirm an identification of a compound, the background
corrected mass spectrum of the compound must be obtained from the
sample.extract and compared with a mass spectrum from a stock or
calibration standard analyzed under the same chromatographic
conditions. It is recommended that at least 25 nanograms of
material be injected into the GC-MS. The criteria below must be
met for qualitative confirmation.
-------
14.4.1 The molecular Ion and all other ions that are present above
10X relative abundance in the mass spectrum of the standard
must be present in the mass spectrum of the sample with
agreement to plus or minus 103S. For example, if the rela-
tive abundance of an ion is 30% in the mass spectrum of the
standard, the allowable limits for the relative abundance
of that ion in the mass spectrum for the sample would be
20-40*.
14.4.2 The retention time of the compound in the sample must be
. within 30 seconds of the same compound in the standard
.solution.
14.4.3 Compounds that have very similar mass spectra can be
explicitly identified by GC-MS only on the basis of reten-
tion time data.
14.5 Where available, chemical ionization mass spectra may be employed
to aid in the qualitative identification process.
14.6 Should these MS procedures fail to provide satisfactory results,
additional steps may be taken before reanalysis. These may include
the use of alternate packed or capillary GC columns or additional
cleanup (Section 11).
15. Method Performance
15.1 The method detection limit (MDL) is defined as the minimum concen-
tration of a substance that can be measured and reported with 99%
confidence that the value is above zero. The MDL concentrations
listed in Table 1 were obtained using reagent water. Similar
results were achieved using representative wastewaters.
•
32
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15.2 This method has been tested for linearity of recovery from spiked
reagent water and has been demonstrated to be applicable over the
concentration range from 10 x MDL to 1000 x MDL.
15.3 In a single laboratory, Battelle Columbus Laboratories, using
spiked wastewater samples, the average recoveries presented in
Table 2 were obtained. Seven replicates of each of two different
wastewaters were spiked and analyzed. The standard deviation of
the percent recovery is also included in Table 2.
33
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REFERENCES
1. "Development of Methods for Pesticides in Wastewaters," Report for EPA
Contract 68-03-2956 (In preparation).
2. ASTM Annual Book of Standards, Part 31, D3694, "Standard Practice for Prep-
aration of Sample Containers and for Preservation," American Society for
Testing and Materials, Philadelphia, PA, p. 679, 1980.
3. "Carcinogens - Workinc with Carcinogens," Department of Health, Education,
and Welfare, Public Health Service, Center for Disease Control, National
Institute for Occupational Safety and Health, Publication No. 77-206,
August, 1977.
4. "OSHA Safety and Health Standards, General Industry," (29 CFR 1910), Occu-
pational Safety and Health Administration, OSHA 2206 (Revised, January
1976).
5. "Safety in Academic Chemistry Laboratories," American Chemical Society
Publications, Committee on Chemical Safety, 3rd Edition, 1979.
6. "Handbook for Analytical Quality Control in Water and Wastewater Laborar
tories," EPA-600/4-79-019, U.S. Environmental Protection Agency, Environ-
mental Monitoring and Support Laboratory - Cincinnati, Ohio 45268, March
1979.
7. ASTM Annual Book of Standards, Part 31, D3370, "Standard Practice for Sam-
pling Water," American Society for Testing and Materials, Philadelphia,
PA, p. 76, 1980.
8. Burke, 0. A., "Gas Chromatography for Pesticide Residue Analysis; Some
Practical Aspects," Journal of the Association of Official Analytical
Chemists, 48, 1037 (1965).
9. Eichelberger, J. W., Harris, L. E., and Budde, W. L., "Reference Compound
to Calibrate Ion Abundance Measurement in Gas Chromatography - Mass Spec-
trometry," Analytical Chemistry. 47, 995 (1975).
34
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TABLE 1. CHROMATOGRAPHIC CONDITIONS AND METHOD DETECTION LIMITS
Parameter Retention Time (min) Method Detection Limit
Column 1Column 2 ("9/L)
Diphenylamine 18.1 19."3 1.6
Column 1 conditions: Supelcoport (100/120 mesh) coated with 2% SP-2250 packed
in a 1.8 rn long x 2 mm ID glass column with helium carrier gas at a flow rate
of 30 mL/min. Column temperature is held at 80°C for 4 minutes, programmed
from 80°C to 300°C at S^C/min and held at 300°C for 4 minutes.
Column 2 conditions: Supelcoport (100/120 mesh) coated with 3% SP-1000 packed
in a 1.8 m long x 2 mm ID glass column with helium carrier gas at a flow rate
of 30 mL/min. Column temperature is held at 80°C for 4 minutes, programmed
from 80°C to 250°C at 80°C/min, and held at 250°C for 4 minutes.
35
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TABLE 2. SINGLE LABORATORY ACCURACY AND PRECISION(a)
•
Parameter
Diphenylamine
Average
Percent
Recovery
120
39
Relative
Standard
Deviation,
%
25
11
••^•••^••••••••MMBMM
Spike
Level
(«g/L)
5.0
50
Number
of
Analyses
7
7
Matrix
Type(b)
1
1
(a) Column 1 conditions were used.
(b) 1 * Columbus secondary POTW effluent,
36
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Dlphenylnralne
r-f-j—r— r"f"i"|-•!••»—»— t—p- r- r—i—r-f"*"''—r " •"" j—i--i—t—v-|~i—r-i—r- -|--r-r--i'-r*i- •••-«•• i—i—|
10.0 21.0 23. a 23. i 27.0 20.0 31,0 33. B 33. B
RETENTION TIME, minutes
KJyure 1. CC-AFD Chromatogram of 100 ng of Dlphenylamlne (Column 1).
-------
u>
00
r-|-
10. B
21. •
22.8
24. • 23.9
RETENTION TIME, minutes
28. 9
Figure 2. CC-FID Cllromatogram of 200 ng of Diphenylamlne (Column 2).
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c~
TECHNICAL REPORT DATA
(Please read Instructions on the reverse bclore completing!
1. REPORT NO. 2.
4. TITLE ANO SUBTITLE
Determination of Diphenylamine in Industrial and
Municipal Wastewaters
7. AUTHORS J>s> Warner, T.M. Engel and
P.J. Mondron
9. PERFORMING ORGANIZATION NAME AND AOORESS
BatteH e Columbus Laboratories
505 King Avenue
Columbus, Ohio 43201
12. SPONSORING AGENCY NAME ANO AOORESS
U.S. Environmental Protection Agency
Environmental Monitoring and Support Laboratory
Cincinnati, Ohio 45268
3. RECIPIENT'S ACCESSION NO.
5. REPORT DATE
6. PERFORMING ORGANIZATION COOS
8. PERFORMING ORGANIZATION REPORT N(
10. PROGRAM ELEMENT NO.
CBECIC
11. CONTRACT/GRANT NO.
68-03-2956
13. TYPE OF REPORT ANO PERIOD COVEREC
14. SPONSORING AGENCY CODE
EPA 600/06
15. SUPPLEMENTARY NOTES
16. ABSTRACT
A method was developed for the determination of diphenylamine in wastewaters.
The method development program consisted of a literature review: determination of
extraction efficiency for each compound from water using roethylene chloride;
development of a deactivated silica gel cleanup procedure; and determination of
suitable gas chromatographic (GC) analysis conditions.
The final method was applied to Columbus POTW secondary effluent in order to
determine the precision and accuracy of the method. The wastewater was spiked with
diphenylamine at levels of 5 ug/L and 50 ug/L. Recovery for diphenylamine at the 5
ug/L level was 120 * 25 percent. Recovery at the 50 ug/L level was 89 ± 11
percent. The method detection limit (MDL) for diphenylamfne in distilled water was
1.6 ug/L. In wastewaters it may be higher due to interfering compounds.
17. KEY WORDS ANO DOCUMENT ANALYSIS
a. DESCRIPTORS
18. DISTRIBUTION STATEMENT
Release to Public
b.lOENTIFI6RS/OPEN ENDED TERMS
19. SECURITY CLASS ( Tins Report}
Nonclassified
2O. SECURITY CLASS (Tint page I
Nonclassified
T f -• <
c. CDSATI Field/Group
21. NO. OF PAGES
39
22. PRICS
EPA form 2270-1 (T?«». 4-77) P*«viou* COITION is OB*ouETe
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