1 Scope
This European Standard specifies a method for the determination of selected organochlorine
pesticides (OCP) (see Table 1), in water samples. The method uses solid-phase extraction with SPE-disks followed
by gas chromatography-mass spectrometry (GC-MS). It is applicable to the analysis
of OCPs in surface water containing suspended particulate matter (SPM) up to 500 mg/l
(whole water samples), drinking water and groundwater. The lower limit of the working
range depends on the matrix, on the specific compound to be analyzed and on the sensitivity
of the mass spectrometric detection unit. For compounds listed in Table 1 the limit of determination (LOQ) is at least 30 % of the corresponding AA-EQS value
(0,000 15 µg/l to 0,1 µg/l) according to the requirements of the European Quality
Standards Directive (Directive 2008/105/EC) for both inland surface waters and other
surface waters.
This method may be used for the analysis of other OCPs not listed in Table 1 or other types of water. However, it is important to verify its applicability before
use.
Table 1
—
Organochlorine pesticides (OCP) determined by this method
|
Substance
|
Molecular formula
|
Molar mass
g/mol
|
EC Number a
|
CAS RN b
|
|---|---|---|---|---|
| Alachlor | C14H20ClNO2 | 269,77 | 240–110–8 | 15972–60–8 |
| Cyclodiene pesticides: | ||||
| Aldrin | C12H8Cl6 | 364,91 | 206–215–8 | 309–00–2 |
|
Dieldrin
Endrin
Isodrin
|
C12H8Cl6O
C12H8Cl6O
C12H8Cl6
|
380,91
380,91
364,91
|
200–484–5
200–775–7
207–366–2
|
60–57–1
72–20–8
465–73–6
|
| DDT-total: | ||||
| op´-DDT | C14H9Cl5 | 354,49 | 212–332–5 | 789–02–6 |
|
pp´-DDT
pp´-DDD
pp´-DDE
|
C14H9Cl5
C14H9Cl4
C14H9Cl4
|
354,49
320,04
318,03
|
200–024–3
200–783–0
200–784–6
|
50–29–3
72–54–8
72–55–9
|
| Hexachlorobenzene (HCB) | C6Cl6 | 284,80 | 204–273–9 | 118–74–1 |
| Hexachlorobutadiene (HCBD) | C4Cl6 | 260,76 | 201–765–5 | 87–68–3 |
| Hexachlorocyclohexane c : | ||||
| alpha-HCH | C6H6Cl6 | 290,83 | 206–270–8 | 319–84–6 |
|
beta-HCH
delta-HCH
gamma-HCH
|
C6H6Cl6
C6H6Cl6
C6H6Cl6
|
290,83
290,83
290,83
|
206–271–3
206–272–9
200–401–2
|
319–85–7
319–86–8
58–89–9
|
| Pentachlorobenzene | C6HCl5 | 250,34 | 210–172–0 | 608–93–5 |
| Trichlorobenzene c : | ||||
| 1,2,3-TCB | C6H3Cl3 | 181,45 | 201–757–1 | 87–61–6 |
|
1,2,4-TCB
1,3,5-TCB
|
C6H3Cl3
C6H3Cl3
|
181,45
181,45
|
204–428–0
203–608–6
|
120–82–1
108–70–3
|
| Endosulfan c : | ||||
| Endosulfan-I (alpha) | C9H6Cl6O3S | 406,93 | – | 959–98–8 |
| Endosulfan-II (beta) | C9H6Cl6O3S | 406,93 | – | 33213–65–9 |