- •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
10.4 Sensitivity
25ppt in routine CGC/MS analysis. 30ppt in routine HPLC analysis.
10.5 Detailed Procedures
10.5.1 Procedure 1: Solid phase extraction/HPLC/DAD
or CGC/MS after methylation
Materials
• Chemicals
acetone, p.a.
acetonitrile, p.a.
ethyl acetate, p.a.
methanol, p.a.
phosphoric acid
phenoxy acid reference compounds
sodium chloride, p.a.
water, HPLC-grade
reagents for diazomethane preparation :
diazald (N-methyl-N-nitroso-4-toluene-sulfonamide)
potassium hydroxide
diethyl ether, p.a.
ethanol, p.a.
210 10 Phenoxy acid herbicides and bentazone
Phenylurea herbicides and pyrazon
11.1 Introduction
Substituted phenylureas and pyrazon are widely used selective herbicides and therefore potential water pollutants. The EC list of priority pollutants includes two phenylurea herbicides, linuron and monolinuron and the methods described in this chapter permit a precise analysis of these compounds, together with other pesticides. Pyrazon (chloridazon), which is also included on the EC priority pollutants list has a different chemical structure, but may also be analysed using the same techniques.
11.2 Compounds
CH,
2. Chloridazon
3. Metoxuron
4. Chlortoluron
5. Monolinuron
6. Diuron
7. Isoproturon
8. Metobromuron
9. Dimcfuron
10. Linuron
ll.Chloroxuron
HC<H,O,
N1ICONICH,),
оси,
Phenylurea herbicides and pyrazon 11
225
11.3 General Procedure
Water samples are extracted by solid phase extraction (SPE) or by liquid-liquid extraction. The extracts are analysed by reverse phase liquid chromatography (RP-HPLC) with diode-array detection (DAD).
11.4 Sensitivity
0.25 ppb in routine analysis.
11.5 Detailed Procedures
11.5.1 Procedure 1: Solid phase extraction/HPLC/DAD
Materials
• Chemicals
phenylurea herbicide reference compounds
acetone, p.a.
acetonitrile, p.a.
sodium acetate
methanol, p.a.
water, HPLC grade
RP-C18 bulk material
florisil
• Solutions
0.002 M acetate buffer (pH6.5) : 28.5g sodium acetate are dissolved in 100ml water. This solution is diluted 1:1000 in water (lml/1). After adjusting to pH6.5 with acetic acid the buffer is filtered through a 0.2 urn membrane filter.
standard solution of phenylurea standards in acetone (400 ug/ml) : 20 mg of each substance is dissolved in 50 ml of acetone.
working standards : the standard solution is diluted in a buffer/acetonitrile mixture (7:3) to yield concentrations of 0.05 ug/ml, 0.10 ug/ml and 0.25|ig/ml.
• Tools
membrane filter, pore size 0.2 um
glass fibre filter paper
empty SPE-columns with polyethylene frits
226 11 Phenylurea herbicides and pyrazon
Triazine herbicides
12.1 Introduction
Triazine herbicides are among the most common agricultural pesticides in use today, their high water solubility leading to fast accumulation in ground water. To help minimize toxic hazards, the legal maximum allowable concentration of triazines in drinking water is limited to less than 100ng/l per individual compound.
In order to determine the two triazines, simazine and atrazine included in the EC priority pollutants list, adequate analytical procedures are required. The following methods may be used to monitor these compounds together with other triazines and some metabolites. By using HPLC with UV detection, other pesticides may be monitored simultaneously.