Comparative Study on Preparation Technology of Evaporation Samples in Pesticide Analysis

Dr. Felix Massat, Benoît Planel*, Antoine Venezia
Laboratoire départemental d'analyses de la Drôme biological laboratory in Valence, France
Introduction
When a highly controlled environment, such as an environmental analysis laboratory, needs to introduce any new instruments or equipment, these new instruments are often rigorously verified to ensure they are equivalent to existing equipment in the laboratory or Better operational performance. This will give you a good idea of ​​any influencing factors in the test method and revalidate the test method if necessary. The recovery of samples (especially very volatile analytes) is the most critical factor in terms of sample concentration and evaporation techniques. In addition to evaluating the operational performance of the Genevac EZ-2 evaporator, the Laboratoire départemental d'analyses de la Drôme (LDA26) laboratory compared the existing two experimental methods in the new equipment evaluation process. This report summarizes the relevant experimental data.

Left: Genevac EZ-2 evaporator
Genevac EZ-2 Performance Benchmark
A pesticide sample (20 mg/l) was added to a mixture of 50 ml of dichloromethane (DCM) and acetone (50:50 by volume of the two substances). An additional drop of pentanol (as solvent) was added to each sample. The sample was evaporated by Genevac EZ-2 (Figure 1) at 35 ° C and concentrated in a drop of pentanol. The experimental procedure uses a special environmental test evaporation method developed by the Tuscan Environmental Protection Agency 1 to selectively evaporate volatile solvents from the analyte to obtain a less volatile solvent component. In a subsequent evaporation experiment, a 1 ml sample dose was made by adding ethyl acetate, and it was injected into a gas chromatograph for analysis using an electron capture detector (GC-ECD). Figure 2 shows the corresponding sample recovery.
Comparative study of Genevac EZ-2 and existing equipment
The Zymark TurboVap Concentration Method and the Simple Fume Hood Air Evaporation Method are two evaporation methods commonly used in the LDA26 laboratory. The EZ-2 preliminary assessment is based on these two conventional experimental methods.
The experimental sample is a volatile environmental analyte. A sample (50 mg/l) was added to a mixture of 50 ml of dichloromethane (DCM) and acetone (volume ratio of the two materials was 50:50). An additional drop of pentanol (as solvent) was added to each sample. Follow the procedure above to evaporate the sample by Genevac EZ-2 or use a Zymark TurboVap concentrator to evaporate the sample and obtain a pentanol drop at 35 °C. In a subsequent evaporation experiment, a 1 ml sample dose was made by adding ethyl acetate and allowed to evaporate to dryness. For samples that have been previously evaporated in Genevac EZ-2, they are again dried in EZ-2 at 35 °C, while samples that have been previously dried in a TurboVap concentrator are required to be in a fume hood. Ventilate and dry again. Water and acetonitrile were then added to the sample and the pH was adjusted to pH 2. Samples were injected into a gradient HPLC system for analysis using a multi-wavelength fluorescence detector (HPLC-Fluor). Figure 3 shows the corresponding sample recovery.
Figure 2 – Multiple analyte recovery rates prepared in Genevac EZ-2
% = recovery SD = standard deviation
Analyte
%
SD
Analyte
%
SD
Analyte
%
SD
123TCB
83
9
HCB
101
11
Pyrimidine
110
17
124TCB
131
16
茚(1,2,3-cd)芘
104
5
Methyl pyrimidine
115
2
135 TCB
105
28
Malathion
100
8
Quetiapine
106
6
2-methylfluoranthene
102
4
Pyripramine
110
15
Pentachloronitrobenzene
100
10
2-methylnaphthalene
94
15
Killing phosphorus
109
7
Tetrachlorobenzene
110
12
è‹Š
101
4
Naphthalene
85
13
Triazolone
120
9
è’½
92
5
Op'DDD
96
8
Triazophos
146
5
Benzo(a)pyrene
90
4
Op'DDE
95
8
Aldosterone
100
9
Benzo(a)pyrene
107
6
Oxidized chlordane
105
1
Diazinon
104
2
Benzo(b)pyrene
102
4
Pentachlorobenzene
95
11
Methyl chlorpyrifos
102
2
Benzo(ghi) 苝
109
6
Philippine
101
28
Methyl parathion
103
7
Benzo(k)pyrene
116
5
Phosphorus
102
5
Killing pine
105
10
Chlorothalonil
71
0
Methyl ester
94
13
Ethyl chlorpyrifos
102
8
Qu
101
5
Methyl sulfone
112
7
Ethyl parathion
89
10
Dibenzo(ah)è’½
108
5
Voltamer
114
6
Methyl bromide
93
8
Dimethoate
116
7
Thiamin
106
12
Venomous
118
twenty one
Acetate
105
8
Pp'DDD
92
8
Ethyl bromide
83
14
Ethylene sulfone
113
7
Pp'DDE
93
8
Trisulfide
95
1
Fenthion
110
8
Pp'DDT
93
8
Methyl azinphos
132
20
Fluoranthene
94
11
Propoxyphosphorus
109
7
Ethyl azinphos
107
9
芴
93
14
芘
117
6
Quick-acting phosphorus
103
4
Figure 3 – Volatile analyte recovery prepared by two-stage evaporation operation by different methods
Genevac & Genevac
TurboVap & Fume hood
Analyte
Test 1
Test2
Test 3
Test 4
Naphthalene
75
79
28
twenty one
2-methylnaphthalene
86
87
40
35
è‹Š
101
101
50
47
芴
100
100
51
50
Philippine
119
120
69
61
è’½
93
94
56
51
Fluoranthene
103
104
74
64
芘
120
121
86
76
2-methylfluoranthene
103
105
83
73
Benzo(a)pyrene
92
93
80
73
Qu
102
102
88
81
Benzo(b)pyrene
105
105
96
87
Benzo(k)pyrene
121
120
110
100
Benzo(a)pyrene
105
105
93
82
Dibenzo(ah)è’½
122
120
112
100
Benzo(ghi) 苝
107
105
96
86
茚和(123-cd)芘
110
110
102
91
Another set of 1 ml samples of ethyl acetate used in the experiments contained different volatile analytes (50 mg/l). An additional drop of pentanol (as solvent) was added to each sample. These samples were placed in Genevac EZ-2 to evaporate at 35 ° C or placed in a fume hood for venting and drying. In a subsequent evaporation test, a 1 ml sample dose was made by adding water and acetonitrile, and its pH was adjusted to pH 2. The sample was injected into the HPLC-Fluor system for analysis. Figure 4 shows the corresponding experimental results.
Figure 4 – Volatile analyte recovery by evaporation in different ways
Genevac
Fume hood
Analyte
Test 1
Test 2
Test 3
Test 4
Naphthalene
93
92
66
61
2-methylnaphthalene
91
92
79
78
è‹Š
103
106
95
97
芴
103
107
96
99
Philippine
120
124
112
116
è’½
96
99
89
92
Fluoranthene
101
104
95
98
芘
122
126
113
116
2-methylfluoranthene
101
106
95
98
Benzo(a)pyrene
91
94
85
86
Qu
99
104
95
96
Benzo(b)pyrene
101
105
96
97
Benzo(k)pyrene
115
120
110
111
Benzo(a)pyrene
106
110
100
100
Dibenzo(ah)è’½
109
113
103
105
Benzo(ghi) 苝
110
115
104
104
茚和(123-cd)芘
104
109
100
101
in conclusion
The new evaporation method using the Genevac EZ-2 vaporizer enables excellent sample recovery, even for highly volatile environmental analytes, yields better sample recovery than previous evaporation methods. The EZ-2 vacuum evaporation method causes the solvent to boil under low temperature conditions to maintain the sample at the boiling point of the solvent. In contrast, when the experiment was carried out using other methods, the sample was always at a high temperature of 35 ° C during the evaporation process. This higher operating temperature increases the rate of evaporation of solvent and volatile components in the sample. By strictly controlling the evaporation conditions in the EZ-2 unit, the solvent can be preferentially removed and the analyte and pentanol are left behind.
references
1. Marsico, Anna Maria, 2006. Improving Analysis of Pesticides – a new method development protocol to increase recovery of volatile compounds. First published in Lab Asia (August 2006 issue), please visit http://www. genevac.org/en/ArticleDetail.asp?S=6&V=1&ProductDownload=81  
About the Author
Dr. Felix Massat is the head of the laboratory; Benoît Planel is a chemist; Antoine Venezia is the head of the R&D department; all three work at the Laboratoire départemental d'analyses de la Drôme biological laboratory, Valence BP118, France ,26904F-91
PDF format Chinese and English original download:
Comparative study on evaporation sample preparation techniques in pesticide analysis (Chinese) Comparative Study on Evaporation Sample Preparation Techniques in Pesticide Analysis (English)

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