Key Benefits:
Regulation of the Minister for Housing, Spatial Planning and the Environment, the Minister for Transport and Water State and the Minister for Agriculture, Nature and Food Quality of 6 April 2010, No BJZ2010006068, Executive Board and Legal Affairs, laying down provisions for the adoption of a monitoring programme for the implementation of Directive No 17 (2). 1999 /60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy (PbEU L 327) and Decision of the European Commission of 30 October 2008 establishing a framework for Community action in the field of water policy (PbEU L 327) for the classification values for the monitoring systems of the Member States resulting from the intercalibration exercise, in accordance with Directive 2000 /60/EC of the European Parliament and of the Council (PbEU L 332) (Scheme monitoring framework for water use)
The Minister for Housing, Spatial Planning and the Environment, the Minister for Transport and Water State and the Minister for Agriculture, Nature and Food Quality,
Having regard to:
Directive No 2000 /60/EC from the European Parliament and the Council of the European Union of 23 October 2000 establishing a framework for Community action in the field of water policy (PbEG L 327);
the European Commission Decision of 30 October 2008 laying down the classification values for the monitoring systems of the Member States resulting from the intercalibration exercise, in accordance with the conditions laid down in Article 3 (2) of the EC Treaty. Directive 2000 /60/EC of the European Parliament and of the Council of the European Union (PbEU L 332), and
The Articles 15 and 16, sixth paragraph, of the Decision on Quality Requirements and Monitoring Water 2009 ;
Decisions:
For the purposes of this arrangement:
Decision: Decision quality requirements and monitoring water 2009 ;
intercalibration decision: European Commission Decision of 30 October 2008 laying down the classification values for the monitoring systems of the Member States resulting from the intercalibration exercise, in accordance with the conditions laid down in Article 3 (2) of the EC Treaty. Directive 2000 /60/EC of the European Parliament and of the Council (PbEU L 332);
quality element: quality element set out in Annex V, paragraph 1.1, to the Water Framework Directive;
Stowa report for natural water types: 'References and measures for natural water types for the Water Framework Directive 2015 -2021', report number 2012-31, ISBN 978.90.5775-9, of the Foundation applied research water management, as published at: http://www.stowa.nl/;
Kewa Locks and Channels report: report 'Description MEP and Dlocks and Channels for the Water Framework Directive 2015 -2021', Report number 2012-34, ISBN 978.90.5775-571.4, of the Foundation applied research on water management, as published at: http://www.stowa.nl/.
For the operationalisation of the general definitions of the ecological status set out in Annex V, Tables 1.2.1 to 1.2.4, of the Water Framework Directive, for the purposes of drawing up and implementing the monitoring programme For each of the types of natural water bodies present in the Netherlands for the quality elements listed in Annex V, paragraph 1.1. of the Water Framework Directive, except for specific pollutants, it shall be intercalibration decision prepared Stowa report for natural water types ed.
1 In the monitoring programme, for the purposes of the application of Article 6, first paragraph, of the Decision Provide that a surface water body for a quality element meets the guide value for the good ecological state of the type of natural surface water body to which the body of water belongs, if the surface water body the monitoring results show:
a. for specific pollutants no higher concentration of one in the Annex the value of the substance mentioned therein shall then contain the value indicated therein for the substance concerned; and
b. for the other quality elements, meets all the values, which for these quality elements for the type of natural surface water body in which the relevant water body is classified, are included in the Stowa Natural water types.
2 In the monitoring programme, for the purposes of the application of Article 6, second paragraph, of the Decision Determine that a strong or artificial surface water body for a quality element meets the requirement of good ecological potential, if the surface water body meets the requirements of the monitoring results; specifications laid down in respect of the quality element in:
(a) the management plan for the waters of the national waters, in the case of the waters of the waters;
b. The regional water plan, if it concerns regional waters.
3 For the classification of a surface water body in a natural surface water body, the characterings are used for the various types of natural surface water bodies included in the Stowa Report for natural water types. In the case of an artificial surface water body, the Stowa-Report for locks and canals may be used for its classification.
1 In the monitoring programme, for the purposes of the classification of a surface water body or a groundwater body in a condition class of the chemical status, the lowest condition class in which the body of water shows the position of the body shall be: monitor results for an in Annex I , below Annex II, to the Decision is classified.
2 In the monitoring programme, for the purposes of the classification of a surface water body in a condition class for specific pollutants, the lowest condition class in which the body of water shows the position of the body shall be monitor results for one in the Annex the substance mentioned in this scheme is classified.
3 In the monitoring programme, for the purposes of the classification of a natural surface water body in a condition class of the ecological state, the boundaries between the Article 16, fifth paragraph, part a, 2 °, of the decision Distinguished condition classes determined in accordance with the Stowa report for natural water types.
4 The monitoring programme shall stipulate that the classification of a strong or artificial surface water body shall take place in a condition class of ecological potential with the application of the 'Manual MEP/GEP', giving a hand-held hand to identification of status, environmental objectives and appropriate packages of non-natural waters of the Project Group Implementation Ceremonies, Ministry of Transport and Water Resources, of November 2005. It shall be based on the good ecological potential established for the body of water in:
(a) in the case of certain waters: the management plan for the waters of the waters;
b. for regional waters: the regional water plan.
The Minister for Infrastructure and the Environment shall adopt the monitoring programme in accordance with Directive 2009 /90/EC of the Commission of the European Union of 31 July 2009 laying down technical specifications for the chemical analysis and monitoring of water conditions under Directive 2000 /90/EC of the European Parliament and of the Council.
This arrangement shall enter into force from the day following the date of issuance of the Official Journal in which it is placed.
This scheme is cited as: The Water Framework Monitoring Scheme.
This arrangement will be set out in the Official Journal.
' s-Gravenhage, 6 April 2010
TheMinister
of Housing, Spatial Planning and the Environment,J.C. Huizinga-Heringa
TheMinister
of Vertimes and Waterstate,C.M.P.S. Eurlings
TheMinister
Agriculture, Nature and Food Quality,G. Verburg
This annex refers to the monitoring of the quality elements of the ecological status, the ecological potential of which is included in Annex V, paragraph 1.1, to the Water Framework Directive as ' specific synthetic pollutants 'and' specific non-synthetic pollutants '. The concentration values set out in the table for specific pollutants have been established in accordance with the procedure laid down in Section 1.2.6 of Annex V to the Water Framework Directive, subject to the conditions laid down in Annex V of this Directive. this procedure has also been taken into account for the toxicity of chemical substances to humans and animals through the aquatic environment and the list of substances listed in Annex VIII to the Water Framework Directive. The classification of a surface water body in one of the condition classes in which the ecological status, or the ecological potential is subdivided according to the monitoring programme, shall be classified according to the descriptions set out in Annex V, paragraph 1.2, Tables 1.2.1 to 1.2.5, to the Water Framework Directive.
EC No
CAS
Substance name
Annual average value of the concentration for surface area waters
(µ g/l)
Expressed as
Annual average value of the concentration for other surface waters
(µ g/l)
Expressed as
Maximum acceptable value of the concentration for surface area waters
(µ g/l)
Expressed as
Maximum acceptable value of the concentration for other surface waters
[ µ g/l]
Expressed as
4 |
7440-38-2 |
Arsenic (and inorganic compounds thereof) |
0.5 |
solved, AC correction possible |
0.6 |
solved, AC correction possible |
8 |
solved, AC correction possible |
1.1 |
solved, AC correction possible |
5 |
2642-71-9 |
Azinphos-ethyl |
0.0011 |
Total |
0.00011 |
Total |
0.011 |
Total |
0.0011 |
Total |
6 |
86-50-0 |
Azinphos-methyl |
0.0065 |
Total |
0.0013 |
Total |
0.014 |
Total |
0.0028 |
Total |
9 |
100-44-7 |
Benzyl chloride (alpha-chlorotoluenes) |
0.02 |
Total |
0.02 |
Total |
n.a. |
n.a. |
||
10 |
98-87-3 |
Benzylidene chloride (alpha, alpha-dichlorotoluene) |
0.0034 |
Total |
0.0034 |
Total |
n.a. |
n.a. |
||
19 |
106-47-8 |
4-Chloaniline |
0.22 |
Total |
0.057 |
Total |
1.2 |
Total |
0.12 |
Total |
49 50, 51 |
CAS No 683-18-1 818-08-6 1002-53-5 |
Dibutyltin (cation) |
0.13 |
Total |
0.09 |
Total |
0.28 |
Total |
0.21 |
Total |
65 |
78-87-5 |
1,2-Dichloropropane |
280 |
Total |
28 |
Total |
1.300 |
Total |
130 |
Total |
69 |
15165-67-0 |
Dichlorprop-P |
1.0 |
Total |
0.13 |
Total |
7.6 |
Total |
0.76 |
Total |
73 |
60-51-5 |
Dimethoate |
0.07 |
Total |
0.07 |
Total |
0.7 |
Total |
0.7 |
Total |
79 |
100-41-4 |
Ethylbenzene |
65 |
Total |
10 |
Total |
220 |
Total |
22 |
Total |
80 |
122-14-5 |
Fenitrothion |
0.009 |
Total |
n.a. |
n.a. |
n.a. |
|||
81 |
55-38-9 |
Fenthion |
0.003 |
Total |
n.a. |
n.a. |
n.a. |
|||
88 |
330-55-2 |
Linuron |
0.17 |
Total |
n.a. |
0.29 |
Total |
n.a. |
||
89 |
121-75-5 |
Malathion |
0.013 |
Total |
n.a. |
n.a. |
n.a. |
|||
90 |
94-74-6 |
MCPA |
1.4 |
Total |
0.14 |
Total |
15 |
Total |
1.5 |
Total |
91 |
93-65-2 |
Mecoprop P |
18 |
Total |
1.8 |
Total |
160 |
Total |
16 |
Total |
94 |
7786-34-7 |
Mevinphos |
0.00017 |
Total |
0.000017 |
Total |
0.017 |
Total |
0.0017 |
Total |
95 |
1746-81-2 |
Monolinuron |
0,15 |
Total |
n.a. |
0,15 |
Total |
n.a. |
||
97 |
1113-02-6 |
Omethoate |
1.2 |
Total |
n.a. |
n.a. |
n.a. |
|||
-99 |
56-55-3 |
Benz (a) anthracone |
0.00064 |
Total |
0.00027 |
Total |
0.28 |
Total |
0.012 |
Total |
3 µ g/kg |
concentration in biota |
3 µ g/kg |
concentration in biota |
|||||||
-99 |
218-01-9 |
Chrysene |
0.0029 |
Total |
0.0014 |
Total |
0.17 |
Total |
0.008 |
Total |
30 µ g/kg |
concentration in biota |
30 µ g/kg |
concentration in biota |
|||||||
-99 |
85-01-8 |
Phenanthrene |
1.2 |
Total |
1.1 |
Total |
7.2 |
Total |
6.7 |
Total |
100 |
56-38-2 |
Parathion |
0.005 |
Total |
n.a. |
n.a. |
n.a. |
|||
-100 |
298-00-0 |
Parathion-methyl |
0.011 |
Total |
n.a. |
n.a. |
n.a. |
|||
105 |
1698-60-8 |
Pyrazon (Chloridazone) |
27 |
Total |
n.a. |
190 |
n.a. |
|||
113 |
24017-47-8 |
Triazophos |
0.001 |
Total |
0.0001 |
0.02 |
0.002 |
Total |
||
114 |
126-73-8 |
Tributylphosphate |
66 |
Total |
6.6 |
170 |
17 |
Total |
||
116 |
52-68-6 |
Trichlorfon |
0.001 |
Total |
n.a. |
n.a. |
n.a. |
|||
125-127 |
900-95-8, 639-58-7, 76-87-9 |
Triphenyltin acetate, Triphenyltin chloride, Triphenyltin hydroxide |
0.00024 |
Total triphenyltin |
0.00023 |
Total triphenyltin |
0.49 |
Total triphenyltin |
0.47 |
Total |
129 |
108-38-3 |
Xylenes |
17 |
total; applies to the sum of isomers |
1.7 |
total; applies to the sum of isomers |
244 |
total; applies to the sum of isomers |
49 |
total; applies to the sum of isomers |
132 |
25057-89-0 |
Bentazone |
73 |
Total |
7.3 |
Total |
450 |
Total |
45 |
Total |
A |
7440-32-6 |
Titanium |
20 |
solved, AC correction possible |
n.a. |
n.a. |
n.a. |
|||
B |
7440-42-8 |
Boron |
180 |
solved, AC correction possible |
n.a. |
450 |
solved, AC correction possible |
n.a. |
||
C |
7440-61-1 |
Uranium |
0.17 |
solved, AC correction possible |
n.a. |
8.6 |
solved, AC correction possible |
n.a. |
||
D |
13494-80-9 |
Tellurium |
100 |
solved, AC correction possible |
n.a. |
n.a. |
n.a. |
|||
E |
7440-22-4 |
Silver |
0,01 |
solved, AC correction possible |
0.081 |
solved, AC correction possible (see note 1) |
0,01 |
solved, AC correction possible |
0.081 |
solved, AC correction possible (see note 1) |
F |
556-67-2 |
Octamethyl-cyclotetrasiloxane |
0.2 |
Total |
0.044 |
Total |
n.a. |
n.a. |
||
7,9 mg/kg |
concentration in biota |
7,9 mg/kg |
concentration in biota |
|||||||
71751-41-2 |
Abamectin |
0.001 |
Total |
0.0000035 |
Total |
0.018 |
Total |
0.0009 |
Total |
|
14798-03-9 |
Ammonium N |
0.304 (see note 2) |
n.a. |
0.608 (see note 2) |
n.a. |
|||||
7440-36-0 |
Antimony |
5.6 |
solved, no AC correction possible |
n.a. |
200 |
solved, AC correction possible |
n.a. |
|||
7440-39-3 |
Barium |
73 |
solved, no AC correction possible |
n.a. |
148 |
solved, AC correction possible |
n.a. |
|||
7440-41-7 |
Beryllium |
0.08 |
solved, AC correction possible |
n.a. |
0.813 |
solved, AC correction possible |
n.a. |
|||
133-06-2 |
Captan |
0.34 |
Total |
n.a. |
0.34 |
Total |
n.a. |
|||
10605-21-7 |
Carbendazim |
0.6 |
Total |
n.a. |
0.6 |
Total |
n.a. |
|||
101-21-3 |
Chlorpropham |
4.0 |
Total |
0.8 |
Total |
43 |
Total |
4.3 |
Total |
|
15545-48-9 |
Chlorotoluron |
0.4 |
Total |
0.04 |
Total |
2.3 |
0.23 |
Total |
||
7440-47-3 |
Chromium |
3.4 |
Sum of chromium (III) and chromium (VI); resolved, AC correction possible |
0.6 |
Sum of chromium (III) and chromium (VI); resolved, AC correction possible |
n.a. |
n.a. |
|||
52918-63-5 |
Deltamethrin |
0.0000031 |
Total |
n.a. |
0.00031 |
Total |
n.a. |
|||
333-41-5 |
Diazinon |
0.037 |
Total |
n.a. |
n.a. |
n.a. |
||||
163515-14-8 |
Dimethanamid-P |
0.13 |
Total |
n.a. |
1.6 1.6 |
Total |
n.a. |
|||
66230-04-4 |
Esfenvalerate |
0.0001 |
Total |
n.a. |
0.00085 |
Total |
n.a. |
|||
22224-92-6 |
Fenamiphos |
0.012 |
Total |
n.a. |
0.027 |
Total |
n.a. |
|||
72490-01-8 |
Phenoxycarb |
0.0003 |
Total |
n.a. |
0.026 |
Total |
n.a. |
|||
23560-59-0 |
Heptenofos |
0.002 |
Total |
0.0002 |
Total |
0.02 |
Total |
0.002 |
Total |
|
138261-41-3 |
Imidacloprid |
0.0083 |
Total |
0.00083 |
Total |
0.2 |
Total |
0.02 |
Total |
|
91465-08-6 |
Lambda-cyhalothrin |
0.00002 |
Total |
n.a. |
0.00047 |
Total |
n.a. |
|||
74223-64-6 |
Metsulfuron-methyl |
0,01 |
Total |
n.a. |
0.03 |
Total |
n.a. |
|||
7440-48-4 |
Cobalt |
0.2 |
solved, no AC correction possible |
n.a. |
1.36 |
solved, AC correction possible |
0.21 |
solved, AC correction possible |
||
7440-50-8 |
Copper |
2.4 (see footnote 3) |
solved, no AC correction possible |
1.1 |
solved, AC correction possible |
n.a. |
n.a. |
|||
67129-08-2 |
Metazachlor |
0.08 |
Total |
0.008 |
0.48 |
Total |
0.048 |
Total |
||
18691-97-9 |
Methabenzthiazuron |
1.8 |
Total |
n.a. |
n.a. |
n.a. |
||||
51218-45-2 |
Metolachlor |
0.4 |
total; value is applicable to S-metolachlor and the racemic mixture |
n.a. |
2.1 |
total; value is applicable to S-metolachlor and the racemic mixture |
n.a. |
|||
7439-98-7 |
Molybdenum |
136 |
solved, no AC correction possible |
n.a. |
340 |
solved, AC correction possible |
n.a. |
|||
23103-98-2 |
Pirimicarb |
0.09 |
Total |
n.a. |
1.8 |
Total |
n.a. |
|||
29232-93-7 |
Pirimiphos-methyl |
0.0005 |
Total |
n.a. |
0.0016 |
Total |
n.a. |
|||
114-26-1 |
Propoxur |
0,01 |
Total |
n.a. |
n.a. |
n.a. |
||||
96489-71-3 |
Pyridaben |
0.0017 |
Total |
0.00094 |
Total |
0.0062 |
Total |
0.0012 |
total (= resolved) |
|
95737-68-1 |
Pyriproxyfen |
0.00003 |
Total |
n.a. |
0.026 |
Total |
n.a. |
|||
7782-49-2 |
Selenium |
0.052 |
solved, no AC correction possible |
n.a. |
24.6 |
solved, AC correction possible |
2.6 |
solved, AC correction possible |
||
83121-18-0 |
Teflubenzuron |
0.0012 |
Total |
n.a. |
0.0017 |
Total |
n.a. |
|||
5915-41-3 |
Terbuthylazine |
0.2 |
Total |
n.a. |
1.3 |
Total |
n.a. |
|||
7440-28-0 |
Thallium |
0.05 |
solved, no AC correction possible |
n.a. |
0.76 |
solved, AC correction possible |
0.34 |
|||
7440-31-5 |
Tin |
0.6 |
solved, AC correction possible |
n.a. |
36 |
solved, AC correction possible |
n.a. |
|||
57018-04-9 |
Tolclofos-methyl |
1.2 |
Total |
n.a. |
7.1 |
n.a. |
||||
7440-62-2 |
Vanadium |
3.5 |
solved, AC correction possible |
n.a. |
n.a. |
n.a. |
||||
7440-66-6 |
Zinc |
7.8 (see footnote 3) |
solved, AC correction possible |
3 |
solved, AC correction possible |
15.6 |
solved, AC correction possible |
n.a. |
1 This value applies to salinity of 34%, corresponding to the salinity in the North Sea. The actual salinity in the body of water shall be taken into account when checking.
2 This value is expressed in mg N (NH4-N + NH3-N) /l and applies to a pH of 7.7 and a temperature of 15 ° C. The monitoring programme shall provide that an adjustment shall be made in checking the results of the monitoring, taking into account the results of the monitoring process. is kept with the current pH and temperature.
3 A correction may be made when testing the results of the monitoring, taking into account water quality parameters that influence the bioavailability of metals.