The purpose of this application note is to outline an automated extraction method utilizing the Atlantic® C18-HC SPE Disk and the Biotage automated and manual SPE solutions for the extraction of organic compounds in drinking water. The first section will highlight the use of the Biotage® Horizon 5000 fully automated extraction system and the method used for this application. Additionally, there will be an Application Modification section that will highlight the use of the Biotage® Horizon 4790 (with data and discussion) and Biotage® VacMaster Disk for this application.
For more than 25 years now, the US has been testing for organic compounds in drinking water using US EPA Method 525.1 The most common version of this method, Method 525.2, is a diverse method with more than 100 compounds listed in a wide range of chemical groups such as pesticides, polychlorinated biphenyls, and polyaromatic hydrocarbons. Method 525.3 offers other changes to the method that may also be of use in making the method more rugged. Additional compounds are evaluated and may be added to the method as the regulatory list is amended every few years.
With increased experience, it has come to be known that certain compounds on the list are difficult to retain using the types of solid-phase extraction (SPE) disks that were available on the market, particularly the more polar compounds. This application note will highlight a new SPE disk which was specifically designed to increase the recoveries of these difficult compounds as well as help to increase the diversity of the traditional 525.2 list to include those compounds which are of concern in today’s society.
» Biotage® Horizon 5000 Automated Extraction System
» Atlantic® C18-HC SPE Disk Agilent
» 6890 GC/MS
|
Step |
Select Solvent |
Volume (mL) |
Purge (s) |
Vacuum |
Saturate (s) |
Soak (s) |
Drain/Elute (s) |
Sample Delay (s) |
|
Condition SPE Disk |
Ethyl acetate |
11 |
60 |
2 |
1 |
60 |
60 |
|
|
Condition SPE Disk |
Dichloromethane |
15 |
60 |
2 |
1 |
60 |
60 |
|
|
Condition SPE Disk |
Methanol |
11 |
60 |
2 |
1 |
60 |
5 |
|
|
Condition SPE Disk |
Reagent water |
15 |
60 |
2 |
1 |
5 |
5 |
|
|
Load Sample |
|
|
|
2 |
|
|
|
45 |
|
Air Dry Disk |
|
|
|
6 |
|
|
120 |
|
|
Elute Sample Container |
Ethyl acetate |
8 |
15 |
2 |
1 |
90 |
60 |
|
|
Elute Sample Container |
Dichloromethane |
8 |
15 |
2 |
1 |
90 |
60 |
|
|
Elute Sample Container |
1:1 DCM/EtOAc |
8 |
15 |
2 |
1 |
90 |
60 |
|
|
Elute Sample Container |
1:1 DCM/EtOAc |
8 |
15 |
6 |
1 |
90 |
120 |
|
|
Step |
Solvent |
Soak Time (s) |
Dry Time (s) |
|
Prewet 1 |
Ethyl Acetate |
60 |
30 |
|
Prewet 2 |
Methylene Chloride |
60 |
30 |
|
Prewet 3 |
Methanol |
60 |
0 |
|
Prewet 4 |
Reagent Water |
5 |
0 |
|
Sample Process |
|
|
|
|
Air Dry |
|
|
60 |
|
Rinse 1 |
Ethyl Acetate |
90 |
30 |
|
Rinse 2 |
Methylene Chloride |
90 |
30 |
|
Rinse 3 |
1:1 Ethyl Acetate: Methylene Chloride |
90 |
30 |
|
Rinse 4 |
1:1 Ethyl Acetate: Methylene Chloride |
60 |
60 |
The data in Table 3 exhibits both excellent recoveries and relative standard deviations (RSDs) for most of the traditional 525.2 target analytes. The concentration of the analytes used in this study was selected to be approximately in the middle of the calibration range.
Of particular note, compounds such as 2,6-dinitrotoluene and 2,4-dinitrotoluene, which normally recover in the 50th to 60th percentile when using SPE disks with the standard loading capacity, were recovered in the 80th to 90th percentile when using this disk. The Atlantic® C18-HC disks, having double the capacity of most standard C18 SPE disks, were able to increase the recoveries by as much as a factor of 1.75 during independent laboratory testing.
Further, highly polar compounds such as caffeine are retained better using a higher capacity disk such as the Atlantic® C18-HC. In this case, caffeine was added to the standard mix because its presence in a water sample is directly related to human interac- tion. By testing for caffeine in water samples, the laboratory could track the impact that humans have on the surrounding water supplies.
Lastly, due to the increase in the disk capacity, it was necessary to monitor some compounds for a potential loss in recoveries. Any losses are due to the increased thickness of the disk and are easy to correct by adding an extra rinse step to fully elute all the target compounds from the SPE disk.
|
Analytes |
Spike Amt. (ug/L) |
LCS 1 (%) |
LCS 2 (%) |
LCS3 (%) |
LCS 4 (%) |
LCS 5 (%) |
LCS 6 (%) |
Average (%) |
RSD (%) |
|
Isophorone |
2 |
83.0 |
88.5 |
92.5 |
99.5 |
95.5 |
100.5 |
93.3 |
7.2 |
|
2-Nitro-m-xylene |
5 |
89.6 |
88.0 |
97.8 |
92.4 |
97.2 |
97.8 |
93.8 |
4.7 |
|
Naphthalene |
2 |
82.0 |
87.0 |
86.5 |
88.5 |
91.5 |
92.5 |
88.0 |
4.3 |
|
Dichlorvos |
2 |
85.0 |
90.5 |
98.5 |
106.5 |
102.5 |
107.0 |
98.3 |
9.1 |
|
Hexachlorocyclopentadiene |
2 |
81.5 |
92.0 |
82.5 |
90.0 |
93.0 |
81.5 |
86.8 |
6.3 |
|
EPTC |
2 |
81.0 |
89.5 |
90.5 |
92.5 |
92.0 |
97.0 |
90.4 |
5.8 |
|
Dimethyl phthalate |
2 |
87.5 |
95.5 |
93.5 |
99.5 |
96.5 |
98.0 |
95.1 |
4.5 |
|
2,6-Dinitrotoluene |
2 |
79.0 |
82.0 |
85.0 |
93.0 |
90.5 |
95.5 |
87.5 |
7.4 |
|
Acenaphthylene |
2 |
80.0 |
87.0 |
85.5 |
92.0 |
91.0 |
94.0 |
88.3 |
5.8 |
|
Acenaphthene |
2 |
84.5 |
92.0 |
89.5 |
94.0 |
94.0 |
94.0 |
91.3 |
4.2 |
|
Chloroneb |
2 |
93.5 |
100.5 |
90.0 |
95.5 |
92.5 |
95.0 |
94.5 |
3.7 |
|
2,4-Dinitrotoluene |
2 |
82.5 |
82.5 |
84.5 |
93.0 |
89.0 |
97.0 |
88.1 |
6.8 |
|
Molinate |
2 |
85.5 |
93.5 |
93.5 |
99.0 |
96.5 |
99.5 |
94.6 |
5.4 |
|
Diethyl phthalate |
2 |
88.5 |
96.0 |
94.5 |
100.5 |
97.0 |
99.5 |
96.0 |
4.5 |
|
Fluorene |
2 |
89.5 |
95.5 |
93.5 |
99.0 |
96.5 |
98.5 |
95.4 |
3.7 |
|
Propachlor |
2 |
85.5 |
96.5 |
97.0 |
102.5 |
87.0 |
102.0 |
95.1 |
7.7 |
|
Trifluralin |
2 |
94.5 |
105.5 |
97.0 |
107.5 |
100.0 |
103.0 |
101.3 |
4.9 |
|
a-BHC |
2 |
93.5 |
102.0 |
93.0 |
97.5 |
94.5 |
96.0 |
96.1 |
3.5 |
|
Hexachlorobenzene |
2 |
92.5 |
98.5 |
88.5 |
93.5 |
91.0 |
92.0 |
92.7 |
3.6 |
|
Lindane (g-BHC) |
2 |
86.5 |
97.5 |
90.0 |
96.0 |
83.0 |
93.5 |
91.1 |
6.2 |
|
Simazine |
2 |
91.5 |
101.0 |
93.0 |
100.0 |
95.0 |
97.5 |
96.3 |
4.0 |
|
Atrazine |
2 |
97.0 |
106.0 |
93.5 |
97.5 |
95.5 |
95.5 |
97.5 |
4.5 |
|
b-BHC |
2 |
89.5 |
96.0 |
93.0 |
97.0 |
92.5 |
95.0 |
93.8 |
2.9 |
|
Pentachlorophenol |
8 |
82.3 |
83.0 |
66.5 |
71.4 |
66.3 |
66.0 |
72.6 |
11.1 |
|
Diazinon |
2 |
81.5 |
90.5 |
71.0 |
67.5 |
67.0 |
78.5 |
76.0 |
12.1 |
|
d-BHC |
2 |
101.5 |
112.0 |
89.5 |
93.0 |
92.5 |
91.5 |
96.7 |
8.9 |
|
Phenanthrene |
2 |
95.0 |
100.0 |
92.0 |
97.5 |
97.0 |
96.0 |
96.3 |
2.8 |
|
Anthracene |
2 |
95.5 |
103.0 |
89.0 |
94.5 |
96.0 |
92.5 |
95.1 |
4.9 |
|
Terbacil |
2 |
106.0 |
107.5 |
86.0 |
90.0 |
86.5 |
89.0 |
94.2 |
10.5 |
|
Chlorothalonil |
2 |
108.0 |
115.0 |
97.5 |
99.5 |
103.5 |
100.0 |
103.9 |
6.3 |
|
Caffeine |
2 |
71.5 |
81.5 |
63.5 |
61.5 |
63.5 |
78.0 |
69.9 |
12.1 |
|
Acetochlor |
2 |
105.0 |
111.5 |
92.5 |
89.0 |
96.5 |
97.5 |
98.7 |
8.4 |
|
Metribuzin |
2 |
109.0 |
110.5 |
93.0 |
98.5 |
101.0 |
102.5 |
102.4 |
6.4 |
|
Heptachlor |
2 |
84.0 |
96.0 |
87.5 |
95.0 |
93.5 |
91.5 |
91.3 |
5.1 |
|
Alachlor |
2 |
106.5 |
111.5 |
93.5 |
94.5 |
98.0 |
88.5 |
98.8 |
8.8 |
|
Prometryn |
2 |
106.5 |
113.5 |
55.0 |
66.0 |
82.0 |
80.5 |
83.9 |
27.0 |
|
Di-n-butyl phthalate |
4 |
101.0 |
111.0 |
93.8 |
92.8 |
93.8 |
94.5 |
97.8 |
7.3 |
|
Bromacil |
2 |
118.5 |
126.5 |
92.5 |
97.5 |
96.5 |
97.5 |
104.8 |
13.4 |
|
Cyanazine |
2 |
111.5 |
116.0 |
93.5 |
97.0 |
97.0 |
96.5 |
101.9 |
9.2 |
|
Malathion |
2 |
110.5 |
118.0 |
101.0 |
96.0 |
100.5 |
104.5 |
105.1 |
7.6 |
|
Metolachlor |
2 |
111.5 |
118.0 |
91.0 |
94.0 |
94.0 |
94.0 |
100.4 |
11.3 |
|
Chlorpyrifos |
2 |
111.5 |
122.5 |
92.5 |
92.5 |
96.0 |
96.0 |
101.8 |
12.1 |
|
Thiobencarb |
2 |
101.0 |
107.5 |
94.5 |
99.0 |
98.0 |
97.0 |
99.5 |
4.5 |
|
Aldrin |
2 |
82.0 |
89.0 |
76.0 |
81.0 |
79.0 |
81.5 |
81.4 |
5.3 |
|
Analytes |
Spike Amt. (ug/L) |
LCS 1 (%) |
LCS 2 (%) |
LCS3 (%) |
LCS 4 (%) |
LCS 5 (%) |
LCS 6 (%) |
Average (%) |
RSD (%) |
|
Parathion |
2 |
107.5 |
112.0 |
85.5 |
89.5 |
88.0 |
88.5 |
95.2 |
12.0 |
|
Heptachlor epoxide B |
2 |
94.5 |
100.5 |
90.0 |
94.0 |
93.5 |
93.0 |
94.3 |
3.7 |
|
Fluoranthene |
2 |
104.5 |
113.0 |
92.0 |
97.0 |
95.0 |
95.0 |
99.4 |
7.9 |
|
g-Chlordane |
2 |
97.0 |
104.5 |
84.5 |
91.0 |
89.5 |
85.0 |
91.9 |
8.3 |
|
Butaclor |
2 |
102.5 |
112.5 |
97.0 |
100.0 |
95.5 |
97.0 |
100.8 |
6.2 |
|
a-Chlordane |
2 |
94.0 |
105.5 |
85.0 |
92.0 |
90.5 |
87.0 |
92.3 |
7.8 |
|
Endosulfan I |
2 |
109.5 |
111.0 |
71.5 |
76.5 |
77.5 |
74.0 |
86.7 |
21.2 |
|
Pyrene |
2 |
106.5 |
115.0 |
90.5 |
96.0 |
96.5 |
95.5 |
100.0 |
9.0 |
|
trans-Nonachlor |
2 |
90.5 |
99.0 |
87.0 |
92.0 |
93.0 |
88.0 |
91.6 |
4.7 |
|
4,4'-DDE |
2 |
100.5 |
108.0 |
90.5 |
97.5 |
96.0 |
94.5 |
97.8 |
6.1 |
|
Dieldrin |
2 |
92.5 |
99.5 |
89.0 |
87.5 |
88.0 |
91.5 |
91.3 |
4.9 |
|
Endrin |
2 |
100.0 |
100.0 |
87.5 |
92.5 |
88.0 |
87.0 |
92.5 |
6.6 |
|
Chlorobenzilate |
2 |
111.0 |
119.5 |
88.5 |
92.5 |
91.5 |
87.5 |
98.4 |
13.7 |
|
Endosulfan II |
2 |
105.5 |
111.0 |
83.0 |
86.5 |
88.5 |
78.5 |
92.2 |
14.1 |
|
4,4'-DDD |
2 |
108.0 |
116.5 |
91.5 |
93.5 |
97.5 |
98.0 |
100.8 |
9.5 |
|
Endrin Aldehyde |
2 |
89.5 |
97.5 |
78.0 |
80.5 |
80.0 |
78.0 |
83.9 |
9.4 |
|
Butyl benzyl phthalate |
2 |
100.5 |
112.5 |
91.5 |
93.5 |
96.5 |
90.5 |
97.5 |
8.4 |
|
4,4-DDT |
2 |
109.0 |
116.0 |
93.0 |
99.0 |
98.0 |
96.0 |
101.8 |
8.6 |
|
Endosulfan Sulfate |
2 |
114.0 |
122.0 |
93.0 |
98.0 |
95.0 |
91.5 |
102.3 |
12.4 |
|
Bis(2-ethylhexyl)adipate |
2 |
105.5 |
114.5 |
89.5 |
95.0 |
91.5 |
94.0 |
98.3 |
9.8 |
|
Hexazinone |
2 |
102.5 |
109.5 |
98.0 |
102.0 |
103.0 |
101.5 |
102.8 |
3.7 |
|
Triphenylphosphate |
5 |
114.2 |
117.0 |
104.2 |
99.0 |
101.0 |
98.2 |
105.6 |
7.6 |
|
Methoxychlor |
2 |
103.0 |
105.5 |
97.5 |
100.5 |
102.5 |
96.5 |
100.9 |
3.4 |
|
Benz(a)anthracene |
2 |
106.0 |
116.5 |
89.0 |
93.5 |
94.5 |
93.5 |
98.8 |
10.5 |
|
Chrysene |
2 |
93.5 |
100.5 |
93.0 |
94.0 |
98.0 |
92.5 |
95.3 |
3.4 |
|
Bis(2-ethylhexyl)phthalate |
2 |
96.5 |
97.0 |
89.0 |
91.0 |
90.0 |
93.5 |
92.8 |
3.6 |
|
cis-Permethrin |
4 |
100.5 |
104.8 |
101.5 |
98.3 |
101.5 |
97.5 |
100.7 |
2.6 |
|
trans-Permethrin |
4 |
97.0 |
101.8 |
101.0 |
102.8 |
101.3 |
98.5 |
100.4 |
2.2 |
|
Di-n-octyl phthalate |
2 |
82.5 |
86.0 |
84.0 |
89.5 |
84.0 |
93.5 |
86.6 |
4.8 |
|
Benzo(b)fluoranthene |
2 |
102.0 |
108.0 |
99.0 |
101.5 |
99.0 |
102.5 |
102.0 |
3.2 |
|
Benzo(k)fluoranthene |
2 |
105.5 |
111.0 |
99.5 |
103.0 |
106.5 |
100.0 |
104.3 |
4.2 |
|
Benzo(a)pyrene |
2 |
104.5 |
110.5 |
105.0 |
106.0 |
109.0 |
105.5 |
106.8 |
2.3 |
|
Perylene-d12 |
5 |
103.0 |
101.6 |
95.2 |
92.6 |
90.6 |
96.6 |
96.6 |
5.1 |
|
Indeno(1,2,3-cd)pyrene |
2 |
123.5 |
130.5 |
115.5 |
115.0 |
115.0 |
120.5 |
120.0 |
5.2 |
|
Dibenz(ah)anthracene |
2 |
127.0 |
138.5 |
119.5 |
119.0 |
119.0 |
124.5 |
124.6 |
6.1 |
|
Benzo(ghi)perylene |
2 |
118.5 |
128.0 |
108.5 |
107.5 |
107.0 |
111.5 |
113.5 |
7.3 |
|
Terbuthlazin |
2 |
100.5 |
109.0 |
94.5 |
81.5 |
77.0 |
98.5 |
93.5 |
12.9 |
|
Penoxaline |
2 |
111.5 |
120.5 |
92.5 |
98.5 |
94.5 |
97.0 |
102.4 |
10.8 |
The Atlantic® C18-HC SPE disk is a simple and straightforward way to increase recoveries for SVOC compounds when testing in water. Its increased capacity allows for a more versatile disk, widening the range of compounds which can be extracted from aqueous samples.
|
Solvent |
Volume (mL) |
Saturate (sec.) |
Soak (sec.) |
Waste Destination |
Drain (sec.) |
|---|---|---|---|---|---|
|
Ethyl Acetate |
11 |
1 |
60 |
Organic |
60 |
|
Methylene Chloride |
15 |
1 |
60 |
Organic |
60 |
|
Methanol |
11 |
1 |
60 |
Organic |
5 |
|
Reagent Water |
15 |
1 |
5 |
Aqueous |
5 |
|
Solvent |
Volume (mL) |
Saturate (sec.) |
Soak (sec.) |
Waste Destination |
Elute (sec.) |
|---|---|---|---|---|---|
|
Ethyl Acetate |
8 |
1 |
90 |
Organic |
60 |
|
Methylene Chloride |
8 |
1 |
90 |
Organic |
60 |
|
1:1 Ethyl Acetate: Methylene Chloride |
8 |
1 |
90 |
Organic |
60 |
|
1:1 Ethyl Acetate: Methylene Chloride |
8 |
1 |
90 |
Organic |
120 |
Literature number: AN101-HOR