- •1.1 Introduction
- •1.2 Sample preparation and clean-up procedures
- •1.2.1 Liquid-liquid extraction
- •1.2.2 Solid phase extraction
- •1.2.3 Purge and trap
- •1.2.5 Derivatization
- •1.2.6 Clean-up procedures
- •1.3 Instrumentation
- •1.3.1 Gas chromatography
- •1.3.1.1 Capillary columns
- •1.3.1.2 Sample introduction systems
- •1.3.2 High performance liquid chromatography
- •1.3.2.1 Hplc columns
- •1.3.2.2 Hplc detectors
- •Volatile organic compounds
- •2.1 Introduction
- •2.2 Compounds
- •2.3 General Procedure
- •2.4 Sensitivity
- •3.1 Introduction
- •3.2 Compounds
- •3.3 General Procedure
- •3.4 Sensitivity
- •3.5.1 Procedure 1: Solid phase extraction/cgc/ms
- •4.1 Introduction
- •4.2 Compounds
- •4.3 General Procedure
- •4.4 Sensitivity
- •4.5 Detailed Procedures
- •4.5.1 Procedure 1: pah analysis using hplc (epa 550.0)
- •5.1 Introduction
- •5.2 Compounds
- •5.3 General Procedure
- •5.4 Sensitivity
- •6.1 Introduction
- •7.1 Introduction
- •7.2 Compounds
- •7.3 General Procedure
- •9.1 Introduction
- •9.3 General Procedure
- •9.4 Sensitivity
- •9.5 Detailed Procedures
- •9.5.1 Procedure 1: Tropolone extraction/cgc/aed or cgc/ms
- •10.1 Introduction
- •10.2 Compounds
- •10.3 General Procedure
- •10.4 Sensitivity
- •10.5 Detailed Procedures
- •11.1 Introduction
- •12.1 Introduction
- •12.2 Compounds
- •13.1 Introduction
- •100-90-80-70-60 50 40 30 20-10-0-
- •20 30 40
- •Iceland
- •Ireland
5.3 General Procedure
Analytes are enriched by solid phase extraction (SPE) and analysed simultaneously by capillary gas chromatography - nitrogen phosphorus detection (CGC/NPD) and capillary gas chromatography - electron capture detection (ECD).
5.4 Sensitivity
5-70ng/l
Individual compounds are listed in Table 5.1.
Compound Detector Detection Recovery Std. Dev. Compound
Limit (ngA) (%) (±%) no. (figures)
Pentachlorobenzene |
ECD |
25 |
42 |
3 |
1 |
Trifluralin |
ECD |
25 |
90 |
13 |
2 |
alpha-HCH |
ECD |
25 |
86 |
13 |
3 |
Hexachlorobenzene |
ECD |
25 |
52 |
5 |
4 |
beta-HCH |
ECD |
25 |
88 |
9 |
5 |
gamma-HCH |
ECD |
25 |
93 |
9 |
6 |
delta-HCH |
ECD |
25 |
78 |
10 |
7 |
Alachlor |
ECD |
25 |
88 |
10 |
10 |
Heptachlor |
ECD |
25 |
74 |
16 |
11 |
Aldrin |
ECD |
25 |
63 |
10 |
13 |
cis-Heptachlorepoxide |
ECD |
25 |
99 |
10 |
14 |
trans-Heptachlorepoxide |
ECD |
25 |
86 |
6 |
15 |
trans-Chlordane |
ECD |
25 |
69 |
22 |
16 |
o,p-DDE |
ECD |
25 |
55 |
7 |
17 |
alpha-Endosulfan |
ECD |
25 |
86 |
11 |
19 |
cis-Chlordane |
ECD |
25 |
72 |
13 |
20 |
p,p-DDE |
ECD |
25 |
43 |
10 |
21 |
Dieldrin |
ECD |
25 |
98 |
12 |
22 |
o,p-DDD |
ECD |
25 |
71 |
7 |
23 |
Endrin |
ECD |
25 |
100 |
9 |
24 |
Table 5.1: Quantitative data in the analysis of halogenated pesticides, PCBs, PBrBs and phosphoric acid esters.
128
5 Pesticides, PCBs and PBrBs
Phenols
6.1 Introduction
The environmental aspects of phenolic compounds have become increasingly important in recent years and both the US EPA and the EC have included phenols on their priority pollutants lists. Phenols in water are routinely monitored by using either high pressure liquid chromatography (HPLC) or capillary gas chromatography with mass spectroscopic detection (CGC/MS).
6.2 Compounds |
|
|
2-chlorophenol |
(EC) |
2 -ethylphenol |
3-chlorophenol |
(EC) |
3-ethylphenol |
4-chlorophenol |
(EC) |
2,3 -dimethylphenol |
2,3-dichlorophenol |
|
2,5 -dimethylphenol |
2,4 -dichlorophenol |
|
2,6 -dimethylphenol |
2,6 -dichlorophenol |
|
3,4 -dimethylphenol |
3,4 -dichlorophenol |
|
3,5 -dimethylphenol |
3,5 -dichlorophenol |
|
2 -chloro- 5 -methylphenol |
2,3,4 -trichlorophenol |
(EC) |
4 -chloro- 2 -methylphenol |
2,3,5-trichlorophenol |
(EC) |
4 -chloro- 3 -methylphenol |
2,3,6-trichlorophenol |
(EC) |
2,4 -dibromophenol |
2,4,5-trichlorophenol |
(EC) |
2,6 -dibromophenol |
2,4,6 -trichlorophenol |
(EC) |
2,4,6-tribromophenol |
4,6 -dichlororesorcin |
|
2,3,5,6 -tetrachlorophenol |
(EC)
2,3,4,5-tetrachlorophenol pentachlorophenol (EC)
(EC) Included on the European Community Priority Pollutants list.
Phenols 6
141
6.3 General Procedure
Phenols are extracted by liquid-liquid or solid phase extraction (SPE) after conversion to their acetates and analysed by capillary gas chromatography/mass spectroscopy (CGC/MS). Alternatively, phenols can be extracted without prior derivatization and analysed by HPLC/diode-array UV detection.
6.4 Sensitivity
5-20ppt by routine CGC/MS. > lppbbyHPLC.
6.5 Detailed Procedures
6.5.1 Procedure 1: Solid phase extraction/CGC/MS
Materials
• Chemicals
phenol reference compounds
2,4,6-trichlorophenol-13CG
acetic anhydride, 99%
potassium carbonate, p.a.
sodium thiosulphate pentahydrate, p.a.
acetone, p.a.
methanol, p.a.
water, HPLC-grade
• Solutions
sodium thiosulphate pentahydrate in water (50 g/1)
standard stock solution of reference substances in acetone (20mg/50ml per compound)
working standards are prepared by appropriate dilution of the standard stock solution with acetone
working standard I 10 ug/ml working standard II 1 ug/ml
• internal standard
2,4,6-trichlorophenol-13Cfi in acetone (lug/ml)
142 6 Phenols
Anilines and nitroaromatics