Introduction
Semi volatile organic compounds (SVOC) have a variety of chemical properties that have been found to cause harmful effects to both humans and the environment. Accurate measurements are challenging to obtain because SVOCs readily adsorb onto surfaces, and are found in common household items such as cleaning agents, personal care products, electrical components, pesticides, water and food. Effects to health depend on the chemical nature of the compound in conjunction with the degree of exposure, yet have been known to include allergenic symptoms, reproductive and endocrine issues. Laboratories around the world measure these compounds in water, soil, and leachates from waste sites. US EPA Method 8270E can be used to determine the concentration of SVOCs extracted from liquid, solid and leachate samples in effort to limit exposure and the spread of these persistent organic pollutants.1
While almost all laboratories test for fewer than the full list of 243 compounds included in the method, typical laboratories will often measure a large suite of 80 to 100 compounds. Compound classes that can be extracted using this method include: polynuclear aromatic hydrocarbons, chlorinated hydrocarbons and pesticides, phthalate esters, organophosphate esters, nitrosamines, halo ethers, aldehydes, ethers, ketones, anilines, pyridines, quinolines, aromatic nitro compounds, and phenols.
This application note will demonstrate the results of Initial Demonstration of Proficiency (IDP) evaluations for compliance with US EPA Method 8270E to deter- mine a list of 114 semi-volatile organic compounds that are neutral, acidic, and basic. In addition to the IDP, a typical groundwater sample will be evaluated and contains a different matrix and particulate content than seen in the IDP. The Matrix Spike (MS)/ Matrix Spike Duplicate (MSD) will demonstrated. Solid phase extraction is described as a suitable sample preparation alternative in Method 8270 and companion method US EPA 3535 outlines the general use of SPE. Suitable sorbent material in disk format for this list of analytes and a modern system for automation will be demonstrated.2
Experimental
The SVOCs in this method were extracted using automated sample preparation solutions for solid phase extraction (SPE), drying and concentration. The samples were extracted using an Atlantic® One Pass Disk (Biotage) which is a mixed mode disk containing several functionalities. Two different pre filters, Atlantic Fast Flow 1 μm and 5 μm (Biotage) with a fine mesh screen were used, as well as a Carbon Cartridge (Biotage) to ensure adequate retention of difficult to obtain light end compounds, such as NDMA and N-Nitrosomethyl ethylamine.
The Fast Flow Disk Holder was used with the samples because groundwater and leachate samples can at times, have varying levels of particulate matter. The Fast Flow Disk Holder uses a 47 mm disk, but allows larger diameter pre-filters to be placed on top to shield the SPE disk from particulates that may cause clogging, and maintain fast sample flow through the disk. The particulates are retained on the filters and washed with solvent during the elution steps, so any compounds that have been adsorbed on the particulates will be included in the extract.
The extraction was completed using the Biotage® Horizon 5000 (previously known as the SPE-DEX® 5000) (Figure 1); an automated extractor which allows various types of liquid samples to be processed directly from the original sample container. The system includes intuitive software for easy programming, and automatic sample and solvent delivery.
The one liter samples were spiked and acidified to pH2 with hydrochloric acid (HCl) and placed on the Biotage® Horizon 5000. Each of the three positions on the Biotage® Horizon 5000 was set up with the One Pass Kit (Biotage). The resulting extracts were dried using DryDisk® Membranes (Biotage) and concentrated with a DryVap™* (Biotage) (Figure 2) for automatic in-line drying and concentration.
The extraction method used with the Biotage® Horizon 5000 is shown in Table 1. The conditions for operating the DryVap™ are shown in Table 2. Most of the steps using the Biotage® Horizon 5000 were completely automated and require no operator intervention. For the few steps where a new flask is required for an elution step, a clear message is shown in the software to make the operation of the system simple to follow.
Figure 1. Biotage® Horizon 5000 (previously known as the SPE-DEX 5000) Extractor with One-pass System
*The DryVap™ system has been discontinued. We recommend using the TurboVap® evaporation systems for achieving equivalent results.
Figure 2. DryVap™ System.
Table 1. Biotage® Horizon 5000 Extraction Method.
|
Step |
Operation |
Message |
Attachment |
|||||
|
1 |
Pause with message |
Part 1 of 3: Neutrals and Acids Elution. Have the Fast Flow Disk Holder with One Pass disk, 1 µm filter, 5 µm filter, top screen over the filters, 250 mL collection flask, and carbon cartridge installed. The down spout of the water in valve must push down on the top screen. Click “Continue” to start Part 1. |
None |
|||||
|
Step |
Operation |
Solvent |
Solvent Vol. (mL) |
Purge Time (s) |
Pump Rate (#) |
Sat. Time (s) |
Soak Time (s) |
Drain Time (s) |
|
2 |
Condition SPE |
Acetone |
40 |
60 |
4 |
2 |
60 |
60 |
|
Step |
Operation |
Sample Flow Rate (#) |
Done Loading Sample Delay (s) |
|
|||||
|
3 |
Load Sample |
5 |
45 |
|
|
|
|
|
|
|
Step |
Operation |
Solvent |
Solvent Vol. (mL) |
Purge Time (s) |
Pump Rate (#) |
N2 Blanket |
Sat. Time (s) |
Soak Time (s) |
Drain Time (s) |
|
4 |
Wash Sample Container |
Reagent Water |
20 |
30 |
4 |
Off |
2 |
5 |
30 |
|
Step |
Operation |
|
Dry Time (s) |
Pump Rate (#) |
N2 Blanket |
|
|
|
|
|
5 |
Air Dry Disk Timer |
|
360 |
6 |
Off |
||||
|
Step |
Operation |
Solvent |
Solvent Vol. (mL) |
Purge Time (s) |
Pump Rate (#) |
N2 Blanket |
Sat. Time (s) |
Soak Time (s) |
Elute Time (s) |
|
6 |
Elute Sample Container |
Acetone |
20 |
20 |
4 |
Off |
2 |
180 |
180 |
|
7 |
Elute Sample Container |
MeCl2 |
17 |
15 |
4 |
Off |
2 |
180 |
180 |
|
8 |
Elute Sample Container |
MeCl2 |
17 |
15 |
4 |
Off |
2 |
120 |
120 |
|
9 |
Elute Sample Container |
MeCl2 |
17 |
15 |
4 |
Off |
2 |
120 |
120 |
|
10 |
Elute Sample Container |
MeCl2 |
17 |
15 |
6 |
Off |
2 |
120 |
180 |
|
Step |
Operation |
Message |
Attachment |
||||||
|
11 |
Pause with Message |
Part 2 of 3: Ion Exchange Elution. Remove the 250 mL collection flask containing the neutrals and acids elution. Stopper the flask and set aside for part 3. Then install a clean 125 mL flask to collect the ion exchange elution. Click “Continue” to Start Part 2. |
None |
||||||
|
Step |
Operation |
Solvent |
Solvent Vol. (mL) |
Purge Time (s) |
Pump Rate (#) |
N2 Blanket |
Sat. Time (s) |
Soak Time (s) |
Elute Time (s) |
|
12 |
Elute Sample Container |
Acetone |
20 |
20 |
4 |
Off |
2 |
0 |
180 |
|
13 |
Elute Sample Container |
1% NH4OH |
20 |
30 |
4 |
Off |
2 |
120 |
120 |
|
14 |
Elute Sample Container |
Acetone |
20 |
20 |
4 |
Off |
2 |
180 |
120 |
|
15 |
Elute Sample Container |
MeCl2 |
17 |
15 |
4 |
Off |
2 |
180 |
180 |
|
16 |
Elute Sample Container |
MeCl2 |
16 |
15 |
4 |
Off |
2 |
120 |
180 |
|
17 |
Elute Sample Container |
MeCl2 |
16 |
15 |
4 |
Off |
2 |
120 |
180 |
|
18 |
Elute Sample Container |
MeCl2 |
16 |
15 |
6 |
Off |
2 |
120 |
180 |
|
Step |
Operation |
Message |
Attachment |
||||||
|
19 |
Pause with Message |
Part 3 of 3: Carbon Cartridge Elution. Remove the carbon cartridge from the tubing lines. Connect the tubing ends together. Using a 20 cc syringe, plunge the carbon cartridge with air through the cap adapter to reseat the carbon bed on the frit. Replace the cap adapter with the funnel cartridge. Replace the disk holder with the cartridge. Replace the 125 mL flask with the 250 mL flask containing the neutrals and acids elution from Part 1. Stopper the 125 mL flask. Click “Continue” to start part 3. |
None |
||||||
|
Step |
Operation |
Dry Time (s) |
Pump Rate (#) |
N2 Blanket |
|
|
|
|
|
|
20 |
Air Dry Disk Timer |
60 |
6 |
Off |
|
|
|
|
|
|
Step |
Operation |
Solvent |
Solvent Vol. (mL) |
Purge Time (s) |
Pump Rate (#) |
N2 Blanket |
Sat. Time (s) |
Soak Time (s) |
Elute Time (s) |
|
21 |
Elute Sample Container |
Acetone |
25 |
20 |
4 |
Off |
3 |
60 |
60 |
|
22 |
Elute Sample Container |
MeCl2 |
17 |
15 |
4 |
Off |
3 |
60 |
20 |
|
23 |
Elute Sample Container |
MeCl2 |
17 |
15 |
4 |
Off |
3 |
60 |
20 |
|
24 |
Elute Sample Container |
MeCl2 |
17 |
15 |
4 |
Off |
3 |
60 |
20 |
|
25 |
Elute Sample Container |
MeCl2 |
17 |
15 |
4 |
Off |
3 |
60 |
20 |
|
26 |
Elute Sample Container |
MeCl2 |
17 |
15 |
6 |
Off |
3 |
60 |
60 |
The samples were measured using GC/MS (6890GC/5975CMS, Agilent Technology). Operational conditions are shown in Table 3. All spiking standard solutions used were from Supelco, Bellefonte, PA. The surrogate mixes were from Restek Corp., Bellefonte, PA. Samples were spiked with 50 µ/L of analytes.
Table 2. DryVap™ System Conditions.
|
Parameter |
Setting |
|---|---|
|
Dry Volume |
200 mL |
|
Heat Power |
|
|
Heat Timer |
OFF |
|
Auto Rinse Mode |
OFF |
|
Nitrogen Sparge |
20 psi |
|
Vacuum |
-7 in. Hg |
Table 3. GC/MS Conditions.
|
Injection |
|
|---|---|
|
Volume |
1 µL |
|
Inlet Temperature |
280 °C |
|
Mode |
Splitless |
|
Gas Type |
Helium |
|
Cartridge |
Zebron™ ZB-Semi volatiles (Phenomenex) |
|
Mode |
Consistent Flow |
|
Oven Program |
45 °C hold for 1 min to 270 °C at 15 °C/min then to 318 °C at 6 °C/min |
|
MS Ions Monitored |
Scan masses 35–550 |
Results and discussion
Prior to implementation of the sample preparation method, Section 9.4 requires each laboratory to complete an Initial Demonstration of Proficiency (IDP) by performing at least four replicate reference samples, taken through the entire Vacuum -7 in. Hg sample preparation and analysis steps. EPA Method 8270E key to analyte list in Section 1.1 suggests that method operation is considered appropriate if average recovery falls between 50–150 %. This note explains that actual recoveries may vary depending on the sample matrix, number of constituents being analysed concurrently, analytical instrumentation, and the preparation method used. The note also includes a list of compounds that have historically been considered problematic (Section 1.4 ). Section 13.1 suggests that performance criteria should be developed on a project-specific basis, and the laboratory should establish in-house QC performance criteria for the application of this method, and use the method criteria is for guidance purposes only.
Table 4 presents data obtained for 4 consecutive runs completed as an IDP study per Section 9.4 with the use of Biotage suite of automated sample preparation equipment. For all compounds except for those of which EPA Method 8270E considers to be problematic (e.g., pyridine, NDMA, hexachlorocyclopentadiene and 2-picoline), average recovery fell in the 50–150% recovery range, and most were better, showing this preparation technique to be acceptable. Standard Deviation for this set of data was found to be 0.77–13 demonstrating reproducibility of results. Blank results are also shown (surrogate recoveries not shown) to indicate the low level of contamination in the process.
Matrix effects on method performance is documented by the Mode Consistent Flow analysis of an unspiked duplicate pair or a matrix spike (MS) and Oven Program matrix spike duplicate (MSD). Since the groundwater samples spike and matrix spike duplicate pair was performed as indicated in the method. Results for the MS/MSD are shown in Table 5 and MS Ions Monitored Scan masses 35–550 meet the criteria listed in Method 8270E for compliance having average percent recoveries fall within 50–150% for all compounds analysed; except those of which EPA Method 8270E considers to be problematic. Relative Percent Difference (RPD) between the data sets was observed to be well below the generally accepted 20% RPD, except for one pair of hexachlorocyclopentadiene (light sensitive) MS/MSD pairs, where the RPD was 25%.
The data presented is normalized to demonstrate the extraction efficiency of compounds in EPA Method 8270E and to eliminate any external sources of error from the analytical instrumentation.
Table 4. Initial Demonstration of Proficiency (IDP).
|
Compounds: |
% Rec |
% Rec |
% Rec |
% Rec |
Average Recovery % |
SD |
|
1,2,4,5-Tetrachlorobenzene |
72.0 |
72.1 |
68.1 |
73.2 |
71.4 |
2.2 |
|
1,2,4-Trichlorobenzene |
72.0 |
71.2 |
68.9 |
70.4 |
70.6 |
1.3 |
|
1,2-Dichlorobenzene |
59.6 |
61.7 |
58.7 |
61.4 |
60.4 |
1.4 |
|
1,3,5,-Trinitrobenzene |
87.0 |
85.6 |
86.9 |
89.7 |
87.3 |
1.7 |
|
1,3-Dichlorobenzene |
53.9 |
57.8 |
55.2 |
57.1 |
56.0 |
1.8 |
|
1,3-Dinitrobenzene |
91.2 |
88.6 |
91.9 |
93.2 |
91.2 |
1.9 |
|
1,4-Dichlorobenzene |
56.4 |
60.0 |
56.6 |
59.5 |
58.1 |
1.9 |
|
1,4-Naphthoquinone |
86.0 |
76.2 |
74.2 |
71.0 |
76.9 |
6.5 |
|
1-Naphthylamine |
99.5 |
84.4 |
96.0 |
91.9 |
93.0 |
6.5 |
|
2,3,4,6-Tetrachlorophenol |
93.2 |
90.8 |
91.3 |
94.3 |
92.4 |
1.6 |
|
2,4,5-Trichlorophenol |
89.6 |
87.5 |
88.9 |
91.1 |
89.3 |
1.5 |
|
2,4,6-Tribromophenol |
93.3 |
92.6 |
94.3 |
95.2 |
93.8 |
1.2 |
|
2,4,6-Trichlorophenol |
91.0 |
88.9 |
89.5 |
91.8 |
90.3 |
1.3 |
|
2,4-Dichlorophenol |
91.0 |
89.0 |
90.2 |
90.5 |
90.2 |
0.83 |
|
2,4-Dimethylphenol |
87.5 |
83.6 |
87.7 |
87.7 |
86.6 |
2.0 |
|
2,4-Dinitrophenol |
80.0 |
79.7 |
79.5 |
84.4 |
80.9 |
2.3 |
|
2,4-Dinitrotoluene |
93.4 |
91.4 |
93.2 |
94.4 |
93.1 |
1.3 |
|
2,6-Dichlorophenol |
89.5 |
87.2 |
87.7 |
90.0 |
88.6 |
1.4 |
|
2,6-Dinitrotoluene |
95.4 |
91.4 |
95.0 |
94.9 |
94.2 |
1.9 |
|
2-Chloronaphthalene |
82.9 |
81.4 |
81.4 |
82.5 |
82.1 |
0.77 |
|
2-Chlorophenol |
79.9 |
78.4 |
77.3 |
78.4 |
78.5 |
1.1 |
|
2-Fluorobiphenyl |
83.4 |
80.1 |
81.7 |
83.3 |
82.1 |
1.6 |
|
2-Fluorophenol |
55.0 |
61.1 |
56.1 |
57.6 |
57.5 |
2.6 |
|
2-Methyl phenol |
81.9 |
83.5 |
82.4 |
83.3 |
82.8 |
0.77 |
|
2-Methylnaphthalene |
81.2 |
80.4 |
79.8 |
80.9 |
80.6 |
0.61 |
|
2-Naphthylamine |
124 |
111 |
118 |
121 |
118 |
5.6 |
|
2-Nitroaniline |
93.5 |
93.1 |
95.5 |
96.4 |
94.6 |
1.6 |
|
2-Nitrophenol |
79.5 |
79.4 |
77.3 |
80.6 |
79.2 |
1.4 |
|
2-Picoline |
44.6 |
48.5 |
45.0 |
47.9 |
46.5 |
2.0 |
|
3,3'-Dichlorobenzidine |
107 |
97.3 |
102 |
106 |
103 |
4.2 |
|
3,3'-Dimethylbenzidine |
129 |
109 |
114 |
126 |
119 |
9.6 |
|
3+4 Methyl phenol |
83.7 |
85.4 |
85.1 |
86.9 |
85.3 |
1.3 |
|
3-Methylcholanthrene |
88.4 |
82.5 |
89.1 |
91.1 |
87.8 |
3.7 |
|
3-Nitroaniline |
110 |
105 |
107 |
110 |
108 |
2.2 |
|
4 Aminobiphenyl |
129 |
128 |
119 |
129 |
126 |
5.0 |
|
4,6-Dinitro-2-methylphenol |
89.6 |
86.9 |
88.6 |
90.3 |
88.9 |
1.4 |
|
4-Bromophenyl phenyl ether |
88.6 |
89.6 |
90.3 |
91.7 |
90.0 |
1.3 |
|
4-Chloro-3-methylphenol |
93.0 |
92.0 |
94.2 |
95.9 |
93.8 |
1.7 |
|
4-Chloroaniline |
124 |
119 |
120 |
124 |
122 |
2.9 |
|
4-Chlorophenyl phenyl ether |
86.7 |
87.1 |
88.5 |
88.6 |
87.7 |
0.96 |
|
4-Nitroaniline |
90.7 |
89.9 |
89.2 |
90.0 |
90.0 |
0.64 |
|
4-Nitrophenol |
89.1 |
87.8 |
92.3 |
92.4 |
90.4 |
2.3 |
|
Compounds: |
% Rec |
% Rec |
% Rec |
% Rec |
Average Recovery % |
SD |
|
4-Nitroquinoline-1-oxide |
93.0 |
91.7 |
91.6 |
96.0 |
93.1 |
2.0 |
|
5-nitro-o-toluidine |
103 |
99.3 |
102 |
104 |
102 |
2.1 |
|
7,12-Dimethylbenz(a)-anthracene |
87.8 |
82.1 |
87.4 |
90.2 |
86.9 |
3.4 |
|
Acenaphthene |
86.2 |
84.4 |
86.5 |
86.0 |
85.8 |
0.94 |
|
Acenaphthylene |
87.5 |
85.4 |
86.7 |
87.1 |
86.7 |
0.89 |
|
Acetophenone |
80.2 |
78.4 |
76.0 |
77.8 |
78.1 |
1.7 |
|
Acetylaminofluorene |
102 |
100 |
100 |
102 |
101 |
0.97 |
|
Aniline |
89.8 |
85.1 |
81.2 |
84.4 |
85.1 |
3.5 |
|
Anthracene |
89.8 |
89.2 |
90.6 |
93.0 |
90.6 |
1.7 |
|
Azobenzene |
91.8 |
89.7 |
91.4 |
92.0 |
91.2 |
1.0 |
|
Benz(a)anthracene |
93.6 |
92.2 |
92.2 |
94.4 |
93.1 |
1.1 |
|
Benzidine |
109.5 |
76.9 |
89.3 |
90.9 |
91.7 |
13 |
|
Benzo(a)pyrene |
90.1 |
88.7 |
88.8 |
92.1 |
89.9 |
1.6 |
|
Benzo(b)fluoranthene |
91.2 |
89.5 |
89.5 |
93.8 |
91.0 |
2.0 |
|
Benzo(ghi)perylene |
94.2 |
91.5 |
91.9 |
95.3 |
93.2 |
1.8 |
|
Benzo(k)fluoranthene |
94.0 |
92.1 |
91.4 |
92.5 |
92.5 |
1.1 |
|
Benzoic acid |
61.2 |
68.7 |
62.9 |
68.5 |
65.3 |
3.8 |
|
Benzyl alcohol |
84.8 |
82.9 |
83.4 |
82.6 |
83.4 |
0.97 |
|
Bis(2-chlorethoxy)methane |
88.5 |
84.3 |
84.8 |
84.9 |
85.6 |
1.9 |
|
Bis(2-chloroethyl)ether |
72.2 |
71.6 |
68.7 |
71.0 |
70.9 |
1.5 |
|
Bis(2chloroisopropyl)ether |
75.2 |
74.1 |
71.0 |
73.2 |
73.4 |
1.8 |
|
Bis(2-ethylhexyl) phthalate |
103 |
103 |
103 |
106 |
104 |
1.3 |
|
Butyl benzyl phthalate |
98.7 |
97.4 |
98.5 |
99.3 |
98.5 |
0.77 |
|
Carbazole |
95.4 |
93.6 |
95.4 |
95.0 |
94.8 |
0.86 |
|
Chrysene |
92.6 |
93.3 |
91.0 |
94.6 |
92.9 |
1.5 |
|
cis-Isosafrole |
85.9 |
84.0 |
83.8 |
84.4 |
84.5 |
0.96 |
|
Dibenz(ah)anthracene |
92.9 |
88.0 |
86.7 |
90.6 |
89.6 |
2.7 |
|
Dibenzofuran |
87.8 |
86.7 |
87.7 |
87.9 |
87.5 |
0.54 |
|
Diethyl phthalate |
96.8 |
94.3 |
97.5 |
97.2 |
96.4 |
1.4 |
|
Dimethyl phthalate |
95.0 |
92.6 |
94.8 |
94.8 |
94.3 |
1.1 |
|
Dimethylaminoazobenzene |
97.3 |
93.4 |
97.3 |
95.9 |
96.0 |
1.8 |
|
Di-n-butyl phthalate |
101 |
99.0 |
102 |
102 |
101 |
1.4 |
|
Di-n-octyl phthalate |
101 |
101 |
102 |
103 |
102 |
0.98 |
|
Dinoseb |
91.1 |
91.8 |
93.1 |
94.1 |
92.5 |
1.4 |
|
Diphenylamine |
94.2 |
90.6 |
94.6 |
93.9 |
93.3 |
1.8 |
|
Ethylmethane Sulfonate |
81.5 |
75.2 |
75.9 |
75.9 |
77.1 |
2.9 |
|
Fluoranthene |
93.3 |
92.8 |
93.4 |
94.9 |
93.6 |
0.93 |
|
Fluorene |
89.2 |
87.3 |
88.1 |
89.3 |
88.5 |
0.96 |
|
Hexachlorobenzene |
88.3 |
90.0 |
89.3 |
92.6 |
90.0 |
1.8 |
|
Hexachlorobutadiene |
54.3 |
54.4 |
50.6 |
54.4 |
53.4 |
1.9 |
|
Hexachlorocyclopentadiene |
49.2 |
45.9 |
39.2 |
40.6 |
43.7 |
4.6 |
|
Hexachloroethane |
53.9 |
58.4 |
53.9 |
57.2 |
55.8 |
2.3 |
|
Hexachloropropene |
54.7 |
55.1 |
52.3 |
54.7 |
54.2 |
1.3 |
|
Indeno(1,2,3-cd)pyrene |
91.5 |
90.0 |
89.0 |
94.1 |
91.1 |
2.2 |
|
Compounds: |
% Rec |
% Rec |
% Rec |
% Rec |
Average Recovery % |
SD |
|
Isophorone |
86.2 |
83.2 |
82.6 |
83.6 |
83.9 |
1.6 |
|
Methapyrilene |
89.5 |
87.0 |
89.0 |
88.8 |
88.6 |
1.1 |
|
Methyl Methane Sulfonate |
54.5 |
49.9 |
58.2 |
60.5 |
55.8 |
4.6 |
|
Naphthalene |
77.0 |
75.4 |
73.6 |
75.3 |
75.3 |
1.4 |
|
NDMA |
38.0 |
39.6 |
47.7 |
50.0 |
43.8 |
5.9 |
|
Nitrobenzene |
78.0 |
76.9 |
73.9 |
76.4 |
76.3 |
1.7 |
|
Nitrobenzene-d5 |
79.0 |
77.0 |
74.5 |
77.2 |
76.9 |
1.8 |
|
N-Nitroso-diethylamine |
69.8 |
69.0 |
67.2 |
69.1 |
68.8 |
1.1 |
|
N-nitroso-di-n-butylamine |
89.9 |
89.0 |
90.6 |
91.2 |
90.2 |
0.94 |
|
N-nitroso-di-n-propylamine |
80.9 |
77.7 |
77.0 |
79.5 |
78.8 |
1.8 |
|
N-Nitrosomethyl ethylamine |
61.0 |
62.2 |
62.2 |
65.3 |
62.7 |
1.8 |
|
N-Nitroso-morpholine |
88.2 |
84.9 |
86.0 |
88.0 |
86.8 |
1.6 |
|
N-Nitroso-piperidine |
84.6 |
81.9 |
81.4 |
83.2 |
82.8 |
1.4 |
|
N-Nitroso-pyrrolidine |
83.4 |
79.8 |
81.8 |
84.5 |
82.4 |
2.0 |
|
o-toluidine |
102 |
95.1 |
91.3 |
97.1 |
96.3 |
4.3 |
|
Pentachlorobenzene |
79.1 |
79.6 |
78.8 |
82.1 |
79.9 |
1.5 |
|
Pentachloroethane |
55.5 |
60.2 |
56.9 |
59.8 |
58.1 |
2.3 |
|
Pentachloronitrobenzene |
92.6 |
91.3 |
89.9 |
93.2 |
91.8 |
1.5 |
|
Pentachlorophenol |
88.2 |
88.8 |
88.2 |
92.8 |
89.5 |
2.2 |
|
Phenacetin |
93.6 |
94.8 |
95.0 |
96.6 |
95.0 |
1.2 |
|
Phenanthrene |
90.1 |
90.2 |
91.3 |
92.6 |
91.0 |
1.2 |
|
Phenol |
56.1 |
57.5 |
58.4 |
57.0 |
57.2 |
0.95 |
|
Phenol-d5 |
56.8 |
57.3 |
58.1 |
57.7 |
57.5 |
0.56 |
|
p-Terphenyl-d14 |
93.9 |
91.9 |
89.3 |
93.9 |
92.3 |
2.2 |
|
Pyrene |
93.1 |
91.6 |
92.7 |
94.2 |
92.9 |
1.1 |
|
Pyridine |
31.4 |
36.1 |
32.5 |
35.6 |
33.9 |
2.3 |
|
Safrole |
88.1 |
84.3 |
87.5 |
86.3 |
86.5 |
1.7 |
|
trans-Isosafrole |
85.8 |
87.2 |
85.3 |
87.2 |
86.4 |
1.0 |
Table 5. Matrix Spike (MS) and Matrix Spike Duplicate (MSD) Results - Ground Water.
|
Compounds: |
MSD-1 Rec |
MSD-1 % Rec |
Avg (%) |
RPD |
MSD-2 % Rec |
MSD-2 % Rec |
Avg (%) |
RPD |
|
1,2,4,5-Tetrachlorobenzene |
78.8 |
65.1 |
72.0 |
9.5 |
72.1 |
72.7 |
72.4 |
0.43 |
|
1,2,4-Trichlorobenzene |
73.5 |
65.0 |
69.2 |
6.1 |
70.9 |
72.9 |
71.9 |
1.4 |
|
1,2-Dichlorobenzene |
61.8 |
54.9 |
58.4 |
5.9 |
61.6 |
66.8 |
64.2 |
4.1 |
|
1,3,5,-Trinitrobenzene |
91.1 |
85.4 |
88.2 |
3.2 |
84.0 |
84.0 |
84.0 |
0.04 |
|
1,3-Dichlorobenzene |
56.8 |
50.2 |
53.5 |
6.2 |
57.4 |
62.7 |
60.0 |
4.4 |
|
1,3-Dinitrobenzene |
96.6 |
88.7 |
92.7 |
4.3 |
89.1 |
86.1 |
87.6 |
1.7 |
|
1,4-Dichlorobenzene |
59.0 |
51.4 |
55.2 |
6.9 |
59.1 |
63.9 |
61.5 |
3.9 |
|
1,4-Naphthoquinone |
86.7 |
72.0 |
79.4 |
9.3 |
76.8 |
75.1 |
76.0 |
1.1 |
|
1-Naphthylamine |
103 |
89.5 |
96.2 |
7.0 |
85.3 |
81.5 |
83.4 |
2.3 |
|
2,3,4,6-Tetrachlorophenol |
94.1 |
87.0 |
90.6 |
3.9 |
89.0 |
88.3 |
88.7 |
0.41 |
|
2,4,5-Trichlorophenol |
89.8 |
85.9 |
87.9 |
2.3 |
87.4 |
86.1 |
86.8 |
0.70 |
|
2,4,6-Tribromophenol |
95.6 |
90.8 |
93.2 |
2.6 |
90.2 |
91.9 |
91.1 |
0.94 |
|
2,4,6-Trichlorophenol |
91.9 |
86.2 |
89.1 |
3.2 |
88.6 |
86.9 |
87.8 |
0.98 |
|
2,4-Dichlorophenol |
92.6 |
86.2 |
89.4 |
3.6 |
87.7 |
87.9 |
87.8 |
0.13 |
|
2,4-Dimethylphenol |
90.0 |
83.9 |
86.9 |
3.5 |
86.6 |
84.8 |
85.7 |
1.1 |
|
2,4-Dinitrophenol |
82.5 |
76.5 |
79.5 |
3.8 |
77.4 |
76.9 |
77.1 |
0.35 |
|
2,4-Dinitrotoluene |
96.1 |
88.1 |
92.1 |
4.3 |
88.6 |
87.4 |
88.0 |
0.69 |
|
2,6-Dichlorophenol |
90.6 |
85.1 |
87.8 |
3.1 |
87.8 |
87.6 |
87.7 |
0.14 |
|
2,6-Dinitrotoluene |
95.5 |
89.8 |
92.7 |
3.1 |
90.5 |
88.6 |
89.6 |
1.1 |
|
2-Chloronaphthalene |
85.9 |
76.7 |
81.3 |
5.6 |
80.4 |
80.6 |
80.5 |
0.12 |
|
2-Chlorophenol |
80.8 |
75.0 |
77.9 |
3.7 |
78.4 |
82.2 |
80.3 |
2.4 |
|
2-Fluorobiphenyl |
87.6 |
79.0 |
83.3 |
5.2 |
83.6 |
83.1 |
83.3 |
0.29 |
|
2-Fluorophenol |
71.5 |
58.6 |
65.1 |
9.9 |
66.7 |
66.3 |
66.5 |
0.36 |
|
2-Methyl phenol |
87.4 |
81.9 |
84.7 |
3.3 |
84.1 |
84.7 |
84.4 |
0.34 |
|
2-Methylnaphthalene |
83.4 |
76.8 |
80.1 |
4.1 |
79.3 |
80.7 |
80.0 |
0.85 |
|
2-Naphthylamine |
127 |
112 |
120 |
6.5 |
109 |
108 |
108 |
0.06 |
|
2-Nitroaniline |
97.5 |
90.5 |
94.0 |
3.7 |
92.3 |
89.6 |
91.0 |
1.5 |
|
2-Nitrophenol |
83.5 |
75.3 |
79.4 |
5.1 |
81.5 |
81.5 |
81.5 |
0.00 |
|
2-Picoline |
47.0 |
42.0 |
44.5 |
5.6 |
47.6 |
49.6 |
48.6 |
2.0 |
|
3,3'-Dichlorobenzidine |
109 |
102 |
105 |
3.3 |
99.9 |
98.2 |
99.1 |
0.88 |
|
3,3'-Dimethylbenzidine |
129 |
117 |
123 |
5.0 |
110 |
102 |
106 |
3.7 |
|
3+4 Methyl phenol |
89.8 |
83.7 |
86.8 |
3.5 |
84.5 |
86.3 |
85.4 |
1.0 |
|
3-Methylcholanthrene |
90.4 |
84.7 |
87.5 |
3.3 |
80.0 |
82.6 |
81.3 |
1.6 |
|
3-Nitroaniline |
111 |
99 |
105 |
5.6 |
104 |
102 |
103 |
0.99 |
|
4 Aminobiphenyl |
127 |
123 |
125 |
1.6 |
123 |
116 |
120 |
2.8 |
|
4,6-Dinitro-2-methylphenol |
91.6 |
86.5 |
89.1 |
2.9 |
83.0 |
83.7 |
83.3 |
0.42 |
|
4-Bromophenyl phenyl ether |
91.5 |
84.9 |
88.2 |
3.7 |
86.1 |
86.4 |
86.3 |
0.13 |
|
4-Chloro-3-methylphenol |
96.7 |
90.1 |
93.4 |
3.5 |
89.5 |
90.2 |
89.9 |
0.42 |
|
4-Chloroaniline |
129 |
117 |
123 |
5.0 |
118 |
117 |
117 |
0.51 |
|
4-Chlorophenyl phenyl ether |
89.4 |
82.2 |
85.8 |
4.2 |
84.3 |
83.9 |
84.1 |
0.25 |
|
Compounds: |
MSD-1 Rec |
MSD-1 % Rec |
Avg (%) |
RPD |
MSD-2 % Rec |
MSD-2 % Rec |
Avg (%) |
RPD |
|
4-Nitroaniline |
95.4 |
85.7 |
90.6 |
5.3 |
87.1 |
85.3 |
86.2 |
1.0 |
|
4-Nitrophenol |
90.7 |
90.1 |
90.4 |
0.3 |
86.2 |
88.3 |
87.2 |
1.2 |
|
4-Nitroquinoline-1-oxide |
97.9 |
89.2 |
93.6 |
4.6 |
86.7 |
87.6 |
87.2 |
0.49 |
|
5-nitro-o-toluidine |
105 |
96.2 |
101 |
4.6 |
95.7 |
93.1 |
94.4 |
1.3 |
|
7,12-Dimethylbenz(a)-anthracene |
88.8 |
83.9 |
86.4 |
2.8 |
79.4 |
84.3 |
81.8 |
3.0 |
|
Acenaphthene |
89.0 |
81.3 |
85.2 |
4.5 |
82.5 |
83.1 |
82.8 |
0.33 |
|
Acenaphthylene |
88.8 |
82.3 |
85.5 |
3.8 |
83.9 |
83.9 |
83.9 |
0.01 |
|
Acetophenone |
80.7 |
72.8 |
76.7 |
5.1 |
77.4 |
80.9 |
79.2 |
2.2 |
|
Acetylaminofluorene |
102 |
96.5 |
99.3 |
2.8 |
96.8 |
96.8 |
96.8 |
0.00 |
|
Aniline |
91.9 |
79.2 |
85.5 |
7.4 |
84.7 |
86.0 |
85.3 |
0.77 |
|
Anthracene |
92.9 |
84.7 |
88.8 |
4.6 |
86.2 |
87.1 |
86.6 |
0.52 |
|
Azobenzene |
93.1 |
86.0 |
89.6 |
4.0 |
87.7 |
86.9 |
87.3 |
0.47 |
|
Benz(a)anthracene |
92.8 |
88.4 |
90.6 |
2.5 |
89.0 |
90.3 |
89.6 |
0.71 |
|
Benzidine |
103 |
88.1 |
95.5 |
7.7 |
70.4 |
80.2 |
75.3 |
6.5 |
|
Benzo(a)pyrene |
90.3 |
85.4 |
87.9 |
2.8 |
85.6 |
86.9 |
86.3 |
0.77 |
|
Benzo(b)fluoranthene |
92.3 |
86.4 |
89.4 |
3.3 |
87.4 |
88.7 |
88.0 |
0.74 |
|
Benzo(ghi)perylene |
93.6 |
87.6 |
90.6 |
3.3 |
90.8 |
90.7 |
90.8 |
0.07 |
|
Benzo(k)fluoranthene |
94.0 |
88.6 |
91.3 |
3.0 |
88.4 |
89.8 |
89.1 |
0.81 |
|
Benzoic acid |
71.2 |
63.9 |
67.6 |
5.4 |
70.4 |
64.7 |
67.6 |
4.2 |
|
Benzyl alcohol |
85.4 |
74.9 |
80.1 |
6.5 |
82.2 |
84.0 |
83.1 |
1.1 |
|
Bis(2-chlorethoxy)methane |
88.6 |
82.1 |
85.3 |
3.8 |
83.7 |
85.8 |
84.8 |
1.2 |
|
Bis(2-chloroethyl)ether |
72.0 |
64.4 |
68.2 |
5.6 |
70.1 |
76.4 |
73.3 |
4.3 |
|
Bis(2chloroisopropyl)ether |
75.3 |
67.2 |
71.3 |
5.7 |
72.6 |
78.1 |
75.4 |
3.7 |
|
Bis(2-ethylhexyl) phthalate |
101 |
98.0 |
99.5 |
1.5 |
95.7 |
98.2 |
97.0 |
1.3 |
|
Butyl benzyl phthalate |
97.5 |
93.3 |
95.4 |
2.2 |
92.3 |
94.9 |
93.6 |
1.4 |
|
Carbazole |
98.0 |
90.8 |
94.4 |
3.8 |
90.8 |
91.1 |
91.0 |
0.21 |
|
Chrysene |
92.9 |
86.8 |
89.9 |
3.4 |
88.3 |
90.1 |
89.2 |
1.0 |
|
cis-Isosafrole |
88.1 |
80.7 |
84.4 |
4.4 |
82.2 |
84.3 |
83.3 |
1.2 |
|
Dibenz(ah)anthracene |
87.4 |
83.2 |
85.3 |
2.5 |
85.6 |
85.9 |
85.7 |
0.20 |
|
Dibenzofuran |
90.2 |
83.3 |
86.7 |
3.9 |
84.1 |
84.5 |
84.3 |
0.19 |
|
Diethyl phthalate |
98.9 |
92.2 |
95.6 |
3.5 |
91.4 |
91.2 |
91.3 |
0.088 |
|
Dimethyl phthalate |
96.6 |
89.6 |
93.1 |
3.7 |
90.5 |
89.3 |
89.9 |
0.66 |
|
Dimethylaminoazobenzene |
96.7 |
93.9 |
95.3 |
1.5 |
89.8 |
92.8 |
91.3 |
1.7 |
|
Di-n-butyl phthalate |
102 |
97.5 |
99.7 |
2.2 |
95.6 |
96.1 |
95.9 |
0.26 |
|
Di-n-octyl phthalate |
99.5 |
95.3 |
97.4 |
2.2 |
93.7 |
96.8 |
95.2 |
1.6 |
|
Dinoseb |
94.4 |
91.7 |
93.1 |
1.5 |
85.8 |
89.4 |
87.6 |
2.1 |
|
Diphenylamine |
95.8 |
88.9 |
92.3 |
3.7 |
89.4 |
88.7 |
89.1 |
0.38 |
|
Ethylmethane Sulfonate |
78.7 |
72.0 |
75.3 |
4.5 |
75.0 |
81.6 |
78.3 |
4.2 |
|
Fluoranthene |
95.9 |
88.1 |
92.0 |
4.2 |
89.8 |
90.1 |
89.9 |
0.17 |
|
Fluorene |
89.4 |
83.5 |
86.5 |
3.4 |
85.0 |
84.5 |
84.8 |
0.27 |
|
Hexachlorobenzene |
91.0 |
84.6 |
87.8 |
3.6 |
87.0 |
87.0 |
87.0 |
0.023 |
|
Hexachlorobutadiene |
63.1 |
47.6 |
55.4 |
14 |
55.1 |
58.7 |
56.9 |
3.1 |
|
Compounds: |
MSD-1 Rec |
MSD-1 % Rec |
Avg (%) |
RPD |
MSD-2 % Rec |
MSD-2 % Rec |
Avg (%) |
RPD |
|
Hexachlorocyclopentadiene |
64.3 |
38.5 |
51.4 |
25 |
46.8 |
46.8 |
46.8 |
0.021 |
|
Hexachloroethane |
56.0 |
49.2 |
52.6 |
6.5 |
55.9 |
61.9 |
58.9 |
5.1 |
|
Hexachloropropene |
60.5 |
50.8 |
55.6 |
8.7 |
56.2 |
59.6 |
57.9 |
2.9 |
|
Indeno(1,2,3-cd)pyrene |
91.6 |
86.4 |
89.0 |
2.9 |
88.4 |
89.4 |
88.9 |
0.54 |
|
Isophorone |
86.5 |
79.7 |
83.1 |
4.1 |
82.8 |
83.3 |
83.0 |
0.31 |
|
Methapyrilene |
90.0 |
84.9 |
87.5 |
2.9 |
84.2 |
84.7 |
84.5 |
0.28 |
|
Methyl Methane Sulfonate |
55.6 |
53.2 |
54.4 |
2.2 |
48.9 |
64.2 |
56.6 |
14 |
|
Naphthalene |
79.1 |
70.4 |
74.8 |
5.8 |
76.3 |
78.0 |
77.2 |
1.2 |
|
NDMA |
41.1 |
39.6 |
40.4 |
1.9 |
37.4 |
52.4 |
44.9 |
17 |
|
Nitrobenzene |
78.2 |
72.2 |
75.2 |
4.0 |
75.8 |
79.6 |
77.7 |
2.4 |
|
Nitrobenzene-d5 |
80.2 |
73.3 |
76.7 |
4.5 |
78.8 |
81.5 |
80.1 |
1.7 |
|
N-Nitroso-diethylamine |
71.1 |
62.6 |
66.9 |
6.3 |
68.4 |
75.1 |
71.8 |
4.7 |
|
N-nitroso-di-n-butylamine |
91.5 |
86.5 |
89.0 |
2.8 |
86.7 |
86.4 |
86.5 |
0.16 |
|
N-nitroso-di-n-propylamine |
80.1 |
79.2 |
79.6 |
0.6 |
75.7 |
80.6 |
78.2 |
3.1 |
|
N-Nitrosomethyl ethylamine |
62.1 |
54.9 |
58.5 |
6.2 |
61.7 |
70.1 |
65.9 |
6.3 |
|
N-Nitroso-morpholine |
88.2 |
80.1 |
84.2 |
4.9 |
82.8 |
88.4 |
85.6 |
3.3 |
|
N-Nitroso-piperidine |
84.4 |
78.3 |
81.3 |
3.8 |
79.6 |
82.8 |
81.2 |
2.0 |
|
N-Nitroso-pyrrolidine |
83.7 |
79.9 |
81.8 |
2.3 |
78.7 |
82.3 |
80.5 |
2.3 |
|
o-toluidine |
101 |
91.4 |
96.3 |
5.1 |
91.6 |
91.7 |
91.7 |
0.0 |
|
Pentachlorobenzene |
83.3 |
73.7 |
78.5 |
6.1 |
77.2 |
78.8 |
78.0 |
1.0 |
|
Pentachloroethane |
58.4 |
51.5 |
54.9 |
6.3 |
59.2 |
64.5 |
61.8 |
4.3 |
|
Pentachloronitrobenzene |
94.1 |
87.2 |
90.7 |
3.8 |
87.5 |
87.7 |
87.6 |
0.13 |
|
Pentachlorophenol |
90.7 |
86.0 |
88.4 |
2.7 |
85.9 |
86.6 |
86.3 |
0.39 |
|
Phenacetin |
97.9 |
91.4 |
94.7 |
3.4 |
91.8 |
90.1 |
90.9 |
0.92 |
|
Phenanthrene |
93.8 |
86.4 |
90.1 |
4.1 |
87.7 |
88.2 |
88.0 |
0.28 |
|
Phenol |
68.7 |
56.2 |
62.5 |
10 |
59.8 |
62.0 |
60.9 |
1.8 |
|
Phenol-d5 |
69.3 |
57.0 |
63.2 |
9.8 |
62.2 |
63.4 |
62.8 |
1.0 |
|
p-Terphenyl-d14 |
92.1 |
86.9 |
89.5 |
2.9 |
89.5 |
90.4 |
89.9 |
0.47 |
|
Pyrene |
94.8 |
86.7 |
90.7 |
4.4 |
89.2 |
89.3 |
89.2 |
0.045 |
|
Pyridine |
32.2 |
29.9 |
31.1 |
3.7 |
34.6 |
35.2 |
34.9 |
0.86 |
|
Safrole |
88.9 |
83.0 |
86.0 |
3.5 |
84.1 |
84.4 |
84.2 |
0.14 |
|
trans-Isosafrole |
89.7 |
82.4 |
86.0 |
4.2 |
87.7 |
85.3 |
86.5 |
1.4 |
Conclusion
The precision and accuracy shown in the Initial Demonstration of Proficiency demonstrate that SPE combined with modern automation for extraction, extract drying and evaporation is an effective solution for a wide range of semi volatile compounds extracted at once from ground water samples. The results are compliant with the method requirements and show a solid base for laboratory use.
Solid phase extraction is an effective extraction technique that reduces the solvent that must be evaporated before GC/MS introduction, reducing costs and time for sample preparation. Disk formats, especially when used with the Fast Flow Disk holder can handle large amounts of particulate and will drastically reduce the possibility of emulsion formation, making the time for extraction more consistent.
This system can be extended to leachate preparation from soil samples or water with additional particulate content, such as wastewater. With today’s modern analytical instrumentation the requirement for one litre samples may not be necessary for all projects and smaller sample (such as 100 mL) preparation has been demonstrated for semi volatile compounds.3
References
- 1. US EPA Method 8270E, https://www.epa.gov/sites/production/files/2017- 04/documents/method_8260d_update_vi_final_03-13- 2017_0.pdf .
- US EPA Method 3535A, https://www.epa.gov/sites/production/files/2015-12/documents/3535a.pdf.
- AN121-HOR, Solid Phase Extraction (SPE) in US EPA Method 625.1, the Performance of Smaller Samples
Literature number: AN124-HOR
