Key Benefits:
Decision of 30 November 2009 laying down rules for the implementation of the environmental objectives of the Water Framework Directive (Decision quality requirements and monitoring water 2009)
We Beatrix, at the grace of God, Queen of the Netherlands, Princess of Orange-Nassau, etc. etc. etc.
On the nomination of Our Minister of Housing, Spatial Planning and the Environment of 30 March 2009, no. BJZ2009022292, Executive Board and Legal Affairs, done on behalf of the Secretary of State for Transport and Water State and our Minister of Agriculture, Nature and Food Quality;
Having regard to:
The Council of State heard (opinion of 3 September 2009, no. W08.09.0109/IV);
Having regard to the further report by Our Minister for Housing, Spatial Planning and the Environment of 26 November 2009, No BJZ2009063271, Executive Board and Legal Affairs, released on behalf of the Secretary of State for Transport and Water State and our Minister of Agriculture, Nature and Food Quality;
Have found good and understand:
1 In this Decision and the provisions based thereon, the following definitions shall apply:
Management plan for the waters of the row: plan as referred to in Article 4.6, first paragraph, of the Water Law which relates to certain waters;
management plan for regional waters: plan as referred to in Article 4.6, first paragraph, of the Water Law which relates to regional waters;
European environmental quality requirement for water: Environmental quality is as intended in Article 5.1, first paragraph, in conjunction with third paragraph, point (c) of the Act , for the implementation of the Water Framework Directive, the groundwater directive, the Priority Substances Directive, or any other EU directive or EU regulation under Article 16 or 17 of the Water Framework Directive or any other binding EU legal act where environmental quality requirements are provided for the protection of groundwater or surface water, and referred to in the Water Framework Directive;
Groundwater body: groundwater body as referred to in Article 2 of the Water Framework Directive, which is Article 4.10 of the Water Decision designated in the regional water plan;
Groundwater Directive: Directive No 2006 /118/EC of the European Parliament and of the Council of the European Union of 12 December 2006 on the protection of groundwater against pollution and deterioration (PbEU L 372);
Artificial surface water body: Under Article 4.5 or 4.10 of the Water Decision surface water body designated as an artificial surface water body in the national water plan or water plan;
Environmental quality: environmental objective, identified as a requirement of: Article 5.1, first paragraph, of the Act ;
monitoring program: monitoring program as intended Article 5.3, third paragraph, of the Act ;
National water plan: plan as referred to in Article 4.1, 1st paragraph, of the Water Law ;
Surface water body: surface water body as referred to in Article 2 of the Water Framework Directive, which is Article 4.5 or 4.10 of the Water Decision designated in the national water plan or water plan;
Our Ministers: Our Minister and, as far as matters are concerned, which are part of his responsibility, our Minister for Economic Affairs;
Regional waters: regional waters as referred to in Article 1.1 of the Water Act ;
Regional water plan: plan as referred to in Article 4.4, first paragraph, of the Water Law ;
Priority substances Directive: Directive 2008 /105/EC of the European Parliament and of the Council of 16 December 2008 on environmental quality standards in the field of water policy amending and subsequently withdrawing the Directives 82 /176/EEC , 83 /513/EEC , 84 /156/EEC , 84 /491/EEC and 86 /280/EEC of the Council, and amending Directive 2000 /60/EC ;
National waters: National waters of the same kind as intended Article 1.1 of the Water Act ;
Heavily changed surface water body: surface water body as such under Article 4.5 or 4.10 of the Water Decision designated in the national water plan or water plan;
River basin district: river basin district as referred to in Article 1.1 of the Water Act , formed by one or more catchment areas and sub-catchment areas forming part thereof;
types of natural surface water body: rivers, lakes, transitional waters or coastal waters as defined in Annex II, point 1.2 of the Water Framework Directive, for which the type-specific reference conditions for the Netherlands have been elaborated under the Ministerial arrangements under Article 15 and in the monitoring programme in accordance with point 1.3 of Annex II to the Water Framework Directive;
Pollutant: the pollutant referred to in Article 1 (31) of the Water Framework Directive, in particular the substances referred to in Annex VIII to that Directive;
Water body: Surface water body or body body;
Water location: the point of departure of surface water or groundwater used in the preparation of water intended for human consumption, or a set of such distracting points;
2 In this Decision and the provisions adopted thereon, the following definitions shall be understood as referred to in Article 2 of the Water Framework Directive: groundwater available, inland waterway, sub-catchment area, ecological status, dangerous substances, good ecological status, good ecological potential, good chemical state of surface water, good chemical state of groundwater, good groundwater status, good quantitative groundwater condition, good surface water state, ground water, groundwater status, coastal waters, quantitative groundwater status, more, environmental objective, environmental quality standard, surface water, surface water status, transitional water, priority substances, river, water catchment area, pollution, water intended for human consumption.
3 In this Decision and the provisions based thereon, the following terms are defined in Article 2 of the groundwater directive: threshold, significant and persistant upward trend.
4 This decision and the provisions adopted thereon mean 'matrix' and 'biotataxone', which is defined in Article 2 of the Directive as priority substances.
1 The European environmental quality requirement for water to be achieved pursuant to this Decision may be derogated only in cases where, under the conditions laid down by the provisions of the Water Framework Directive, the conditions under which this decision may be taken are to which reference is made in this Decision.
2 If a body of water applies more than one environmental objective as a result of this decision or other regulatory action, the strictest application shall apply.
3 A European environmental quality standard for water to be achieved pursuant to this Decision may be derogated from in respect of the relevant period if:
a. The condition of the body of water does not fall backwards according to Article 16 ,
(b) all the conditions of Article 4, fourth and eighth paragraph, of the Water Framework Directive have been fulfilled; and
c. the reason for the derogation for that body of water is indicated in the management plan for the waters of the national waters, in the case of national waters, or the regional water plan, if the regional waters or groundwater are concerned.
4 A derogation from a European environmental quality for water to be achieved pursuant to this Decision may be waived if:
a. The condition of the body of water does not fall backwards according to Article 16 ,
(b) the body of water concerned has been affected by human activities to such an extent that its natural condition is such that the attainment of the guide value is not feasible or is disproportionate;
(c) all the conditions laid down in Article 4, fifth and eighth paragraph, of the Water Framework Directive have been fulfilled; and
d. the reason for the derogation for that body of water is indicated in the management plan for the waters of the waters, in the case of national waters, or the regional water plan, if they are regional waters or groundwater.
5 A good ecological status or a good groundwater status may be further deviated from a European environmental quality for water, to be achieved pursuant to this Decision, if:
a. the failure to achieve it results from new changes in the physical characteristics of a surface water body or changes in the position of a groundwater body;
(b) all the conditions of Article 4, seventh and eighth paragraph, of the Water Framework Directive have been fulfilled; and
c. the reason for the derogation for that body of water is indicated in the management plan for the waters of the national waters, in the case of national waters, or the regional water plan, if regional waters are concerned.
6 For an artificial or highly altered surface water body, the second, third and fourth members shall apply mutatis mutandis with respect to the good ecological potential established for a surface water body according to Article 6, second paragraph .
7 A derogation from a European environmental quality requirement for water to be achieved pursuant to this Decision may be waived if:
a. the derogation is due to a pollution source located outside the Netherlands,
(b) compliance with the guide value due to transboundary pollution is not possible; and
(c) all the conditions laid down in Article 6 (1) (c) and (2) of the Directive are fulfilled.
1 For the purposes of applying Article 5.2b, fourth paragraph, of the Act A temporary deterioration in the condition of a water body shall be permitted if:
a. this is the result of circumstances occurring by natural cause or force majeure, which were exceptional or unreasonably foreseeable, particularly extreme flooding and long drier periods, or due to natural causes. circumstances caused by unforeseeable accidents not foreseeable,
(b) all the conditions laid down in Article 4, sixth and eighth paragraph, of the Water Framework Directive have been fulfilled; and
c. the reason for the derogation for that body of water is given in the next management plan for the waters, in the case of national waters, or the next regional water plan, if the regional waters or groundwater are concerned.
2 For the purposes of applying Article 5.2b, fourth paragraph, of the Act A deterioration in the condition of a water body shall be permitted if:
a. failure to prevent that decline is due to new changes in physical characteristics of a surface body or changes in the position of groundwater bodies, or failure to prevent deterioration of a very good body. condition of a surface water body to a good condition is the result of new sustainable activities of human development,
(b) all the conditions laid down in Article 4, seventh and eighth paragraph, of the Water Framework Directive have been fulfilled; and
c. the reason for the derogation for that body of water is indicated in the management plan for the waters of the national waters, in the case of national waters, or the regional water plan, if the regional waters or groundwater are concerned.
1 Unless application is made of a possibility to deviate within the meaning of the Articles 2 (3) to (7) , 3 or 6, second paragraph , when determining the national water plan, the management plan for the waters, a regional water plan or a management plan for the regional waters, the plan for each surface water body included in the plan shall be the next European project. Environmental quality has been achieved for water: a good surface water condition has been achieved with effect from 22 December 2015.
2 By way of derogation from paragraph 1, a plan as referred to in that paragraph shall apply to a period starting after 21 December 2015, that a good chemical status of a surface water body, as far as the substances are concerned, is correct. regards for which this is in Annex I This Decision has been reached with effect from 22 December 2021.
3 By way of derogation from paragraph 1, a plan as referred to in that paragraph shall apply to a period commensurate after 21 December 2015, that a good chemical condition of a surface water body shall, to the extent that it is the Article 5a the quality of the environment has been achieved as from 22 December 2021.
4 In a case as referred to in Article 3 (8) , of the Directive priority substances, by derogation from the second paragraph instead of the date 21 December 2015 the date 21 December 2018 and instead of the date 22 December 2021 the date 22 December 2027.
5 By way of derogation from paragraph 1, a plan as referred to in that paragraph shall apply to a period starting after 21 December 2021, that a good chemical status of a surface water body, as far as the substances are concerned, is correct. regards for which this is in Annex I This Decision has been reached with effect from 22 December 2027.
6 For surface water bodies designated as shellfish in the national water plan, a good surface water condition also means that no bacterial contamination is present in shellfish to an extent that may be harmful to the surface water. public health.
7 A good surface water condition as referred to in the first paragraph shall mean that both the chemical status and the condition of the Articles 5 and 5a , as the ecological condition, intended in Article 6 , adopted in accordance with the provisions of those Articles.
A surface water body is in a good chemical condition if it has been established in accordance with the monitoring programme to meet the European environmental quality requirements for water mentioned in Annex I to this Decision.
In adopting the national water plan, the management plan for the waters, a regional water plan or a management plan for regional waters, the plan for each body of water included shall be the following European environmental quality: For water, the concentration of a priority substance which tends to accumulate in sediment or in biota, determined in accordance with the monitoring programme, is not significant at the end of the plant period in sediment and biota increased.
1 A surface water body is in good ecological condition if it is established in accordance with the monitoring programme that for the quality elements of the natural surface water body to which the surface water body is in Annex V, paragraph 1.1, in the Water Framework Directive, the following European environmental quality requirements for water have been met:
the general definitions of the good ecological status set out for the type concerned in Annex V, Section 1.2, Tables 1.2.1 to 1.2.4, to the Water Framework Directive.
2 The European environmental quality requirements for water referred to in paragraph 1 may be derogated from provided that:
a. The body of an artificial body of water or a strong body of water; and
b. for that body of water, indicating the reason for the derogation, a good ecological potential is established in the management plan for the waters of the waters, in the case of certain waters, or the regional water plan, if the regional waters is.
3 A good ecological potential as referred to in paragraph 2 given the physical conditions resulting from the artificial or highly altered characteristics of the surface water body, as far as possible correspond to the European Environmental quality requirements for water for biological, hydromorphological and physico-chemical quality elements of the good ecological status of the most comparable types of natural surface water body. It shall be determined in accordance with the general definitions of good ecological potential set out in Annex V, Section 1.2, Table 1.2.5, to the Water Framework Directive.
1 Unless application is made of a possibility to deviate within the meaning of the Articles 2 (3) to (7) , 3 or 6, second paragraph , when establishing a regional water plan, that the plan for each groundwater body included is the following European environmental quality for water: a good groundwater status has been achieved as of 22 December 2015.
2 A good condition as referred to in paragraph 1 shall mean that both the quantitative and quantitative conditions referred to in the first paragraph shall be Article 8 , if the chemical is controlled by Article 9 , adopted in accordance with the provisions of those Articles.
A groundwater body is in a good quantitative condition if all the conditions of Annex V, point 2.1.2, to the Water Framework Directive are met.
A groundwater body is in a good chemical condition if it is established in accordance with the monitoring programme:
a. all the conditions set out in point 2.3.2 of Annex V to the Water Framework Directive and the European environmental quality requirements for water referred to in Annex V, Annex II , Tables 1 and 2 to this Decision;
b. In one or more monitoring points, a European environmental quality requirement for water referred to in subparagraph (a) but of the Member States has been confirmed by an appropriate examination in accordance with Annex III to the Groundwater Directive comply with all the conditions laid down in Article 4 (c) and (5) of that Directive.
1 Unless a derogation provided for in this Decision applies, the adoption of a regional water plan for each groundwater body included in this Decision shall be aimed at attaining the following European environmental quality for water: With effect from 22 December 2009, a groundwater body does not find any significant and persistant rising trends in the concentrations of pollutants, groups of pollutants or indicators of pollution, which are significant be risk-risk for the quality of an aquatic or terrestrial ecosystem, human health, or for the legitimate use, actual or potential, of the aquatic environment.
2 A significant and continued upward trend is a significant risk of damage as referred to in paragraph 1, if the starting point is or is likely to be exceeded for a trend reversal, and not in accordance with the provisions of Article 5 (2), measures required by the groundwater directive are being taken.
3 The starting point for a trend reversal, referred to in the second member, is 75% of European environmental quality requirements for water in Annex II , Tables 1 and 2 are incorporated in this Decision.
4 The European environmental quality standard for water to be achieved pursuant to paragraph 1 may be waived in relation to the percentage referred to in paragraph 3 if:
(a) is a situation referred to in point 1 (c) of Part B of Annex IV to the groundwater directive;
b. a higher percentage is indicated in the regional water plan for a groundwater body;
c. is satisfied with all the conditions of the provision mentioned in subparagraph (a); and
d. the reason for the derogation is given in the plan referred to in subparagraph (b).
For the application of Article 12 'a water-wind site' means a location as such in the management plan for the waters, in the case of national waters, or the regional water plan, if the regional waters or groundwater are concerned.
1 Unless a derogation as referred to in this Decision applies, the adoption of the national water plan, the management plan for the waters, a regional water plan or a management plan for regional waters shall be established for each of the following: water-wind site from which surface water is taken from, aimed at achieving the European environmental quality requirements for water included in the extracted water in Annex III to this Decision.
2 The European environmental quality requirements for water referred to in paragraph 1 shall be met with effect from 22 December 2009.
3 When establishing a plan referred to in paragraph 1, the following European environmental quality requirement for water shall be sought: an improvement in quality, determined in accordance with the monitoring programme, of each of the following: Surface water body or groundwater body in which a water-winning site is located, and any surface water body containing it, from which water is extracted from a water-wind site after the use of the soil, with a view to the level of purification of the water source The withdrawn water required for the preparation of for human consumption of water to be reduced.
4 The European environmental quality requirement for water referred to in paragraph 3 shall be: Article 2 Not applicable.
When determining the national water plan, the management plan for the waters, a regional water plan or a management plan for the regional waters, the plan for each body of water containing a water-wind location shall be the plan for each of the areas listed in Annex I to this Regulation. The following European environmental quality has been achieved for water: there is no question of deterioration of the quality of the body of water determined in accordance with the monitoring programme, which is at risk of the level of purification to be used in the preparation of water intended for human consumption, shall be increased.
1 Our Ministers shall adopt a monitoring programme in accordance with the provisions of the Water Framework Directive, the groundwater directive and the priority substances for each river basin district. The programme shall include an indication of the monitoring points, and a description of the following:
a. Monitoring of the condition of a body of water, as far as substances and quality elements are concerned, relevant to the condition of the body of water;
b. Monitoring of the emerging substances included in the Rps Attention List referred to in Article 8b (1) (1) of the Priority Substances Directive (hereafter: Rps Attention List);
c. Monitoring of the substances identified as indicators of a potential threat to the quality of surface water or groundwater being removed from the preparation of water intended for human consumption;
d. monitoring of trends with respect to the concentrations of substances;
e. monitoring of the quantitative status of a groundwater body, including an assessment of the available groundwater supply,
f. interpretation and presentation of monitoring results;
g. Classification of a water body in a condition class,
h. reporting on the monitoring results and the conclusions attached thereto; and
i. Determination of the condition class in which a body of water is located, per substance and quality element, for the purposes of the application of Article 16 ,
to obtain representative monitoring data, providing a coherent overall picture of the condition of water bodies within the river basin district.
2 In the monitoring programme, in accordance with point 1.3.4 of Annex V to the Water Framework Directive, statistical methods may be used, including a percentile calculation, so that an acceptable level of reliability and accuracy is ensured when determining whether a European environmental quality standard for water established in this Decision is met. The statistical methods shall comply with the rules laid down in accordance with the procedure laid down in Article 9 (2) of the Directive.
3 Where the average value of a substance listed in Annex I to this Decision, in accordance with the monitoring programme for a body of water, is lower than the limit of determination and the limit of determination of the substance in question, Annex I In exceeding European environmental quality standards for water in excess of that decision, the average value determined for that substance is considered to be 'below the limit of determination' and not taken into account in the assessment of the chemical condition of the water body.
4 The monitoring programme shall be reviewed and updated in cases where it is required by the Water Framework Directive.
5 By way of derogation from the first paragraph, a part of the monitoring programme for monitoring for further examination, in cases referred to in Annex V, point 1.3.3, in the Water Framework Directive, or on monitoring for additional information shall be provided for: trend assessment, in cases referred to in Article 5 (5) of the Groundwater Directive, subject to the provisions of those Directives adopted by the Governing Body under the provisions of Article 5 (1) of the Directive on groundwater. Article 14 has been responsible for monitoring the relevant water body.
6 Of a monitoring programme or part of a monitoring programme as referred to in the fourth paragraph and an update of that programme or part shall inform our Minister of Public Knowledge.
For the purposes of the implementation of the monitoring programme, each of them shall be responsible for:
a. for surface water bodies: the administrative bodies competent to obtain a permit under Article 6.2, First paragraph, of the Water Law to be granted;
b. For groundwater bodies: deputed states.
In accordance with the provisions of the Water Framework Directive, and in particular Annex V, point 1.2.6, to that Directive, the groundwater directive and the priority substances directive may be subject to rules by means of a ministerial arrangement. relation to the components of the monitoring programme mentioned in Article 13, first paragraph .
1 The monitoring programme shall, subject to the second paragraph, indicate how the end of the period of planning for each body of water is to be determined or fulfilled during the planning period. Article 5.2b, fourth paragraph, of the Act .
2 There is no compliance with the obligation to prevent deterioration of the condition of a water body as intended Article 5.2b, fourth paragraph, of the Act in the case of a substance or a quality element which is subject to a European environmental quality requirement for water under this Decision, if:
a. The condition of a water body has ended up in a lower condition class; or
b. The quality of the water body in the lowest condition class, determined in accordance with the monitoring programme, has deteriorated.
3 The second paragraph shall apply, in so far as it concerns substances for which it is Annex I to this Decision, with effect from 22 December 2021.
4 The classification of a surface water body in a condition class corresponds to the lowest condition class in which the chemical status, the ecological status, is the ecological potential, is in the region.
5 The classification of a body of groundwater in a condition class corresponds to the lowest condition in which the quantity of the soil, the chemical and the chemical status, is in the state.
6 For the purposes of applying the second paragraph, the following condition classes shall be distinguished:
a. for surface water bodies:
1 °. as regards the chemical situation, the condition class as referred to in Article 5 , or not good,
2 °. as for the ecological condition: the condition class very good, well as intended in Article 6, first paragraph , moderate, inadequate or bad, determined for the type of natural surface water to which the surface water body belongs, as defined in Annex V, Section 1.2, Tables 1.2.1 to 1.2.4, to the Water Framework Directive;
3 °. as regards the ecological potential, if applicable: the condition class good as intended in Article 6, third paragraph , moderate, inadequate or bad, as defined in Section 1.2, Table 1.2.5, to the Water Framework Directive, in accordance with what is stated in the plan referred to in point (b) of Article 6 (2);
b. for groundwater bodies:
7 The rules of application of this Article shall be subject to a ministerial arrangement.
1 The period referred to in Article 5.1, fifth paragraph, of the Act , shall be six years, unless a European environmental quality requirement for water has previously been revised for the purpose of implementing Article 11, fifth paragraph, fourth indent of the Water Framework Directive.
2 The first sentence of Article 5.2, third paragraph, of the Act shall not apply in respect of the European environmental quality requirements for water laid down in this Decision.
An amendment to the Water Framework Directive under Article 20 of the Directive, an amendment to the groundwater directive pursuant to Article 8 of the directive or an amendment to the Directive on priority substances pursuant to Article 3 of the directive for the purposes of this Decision and the provisions based thereon, shall apply from the date of implementation of the amending Directive concerned, except where a Ministerial Order published in the Official Journal of the European Union provides that: other time shall be fixed.
1 The paragraphs of the Decision quality requirements and monitoring water lapse in time to be determined by royal decree, which may be determined differently for the different paragraphs.
2 The Decision quality requirements and monitoring water shall be withdrawn.
This Decision shall enter into force on a date to be determined by the Royal Decree, which may be adopted in a different way for the various articles or parts thereof.
This Decision is cited as: Decision quality requirements and monitoring water 2009.
Charges and orders that this Decision will be placed in the Official Journal by means of the note of explanatory note accompanying it.
' s-Gravenhage, 30 November 2009
Beatrix
The Minister for Housing, Spatial Planning and the Environment,
J. M. Cramer
The Secretary of State for Transport and Water,
J. C. Huizinga-Heringa
The Minister of Agriculture, Nature and Food Quality,
G. Verburg
Published the 19th January 2010The Minister of Justice,
E. M. H. Hirsch Ballin
The columns have been successively indicated:
1. the number of the priority substances in the Water Framework Directive and the Priority Substances Directive
2. CAS number (see note 1)
3. the EU number (see note 2)
4. the name of the priority substance and the designation of priority substances as a priority hazardous substance (for the relevant substance identified by (X)). Where groups of substances are selected, typical examples of these shall be used in determining environmental quality requirements, unless otherwise specified.
5 and 6. JG-MKE: European environmental quality requirement for water expressed as an annual average (JG) in the unit [ μg/l], which applies to the total concentration of all isomers. In applying the JG-MKE, the arithmetic mean of the concentrations measured at different times during the year during each representative monitoring point for the water body is not above the standard. The JG MKE is expressed as the total concentration in the complete water sample. Calculation of the arithmetic mean, the method of analysis to be used and how an MKE is applied in the absence of an appropriate analytical method which fulfils the minimum performance characteristics shall be in accordance with implementing instruments containing technical specifications for the chemical control and quality of analytical results in accordance with the Water Framework Directive.
By way of derogation from the above, the JG-MKE for cadmium, lead, mercury and nickel (metals) refer to the concentration in question. This is the dissolved phase of a water sample obtained by filtration over a 0.45 μm filter or equivalent pre-treatment. The monitoring programme may provide that an adjustment can be made to the JG-MKE monitoring results, taking into account:
(a) natural background concentrations for metals and their compounds, if they prevent compliance with environmental quality requirements; and
(b) the hardness, pH or other water quality parameters affecting the bioavailability of metals, where the concentration of bioavailable is determined by the use of appropriate bioavailability model.
7 and 8. MAC-MKE: European environmental quality requirement for water, expressed as a maximum acceptable concentration (MAC) in the unit [ μg/l]. For the MAC-MKE application, none of the representative monitoring points for the water body shall apply. concentration above the standard. When indicated for the MAC-MKE "nvt" (not applicable), JG MKE values are supposed to provide protection against short-term pollution peaks in continuous discharges, as these are significantly lower than those on the basis of the acute toxicity-derived value. The MAC-MKE is expressed as the total concentration in the full water sample. By way of derogation from the above, the MAC-MKE for cadmium, lead, mercury and nickel (metals) refer to the concentration in question. This is the dissolved phase of a water sample obtained by filtration over a 0.45 μm filter or equivalent pre-treatment. The monitoring programme may provide for a correction to be made to the MAC-MKE when assessing the results of the monitoring process, taking into account:
(a) natural background concentrations for metals and their compounds, if they prevent compliance with environmental quality requirements; and
(b) the hardness, pH or other water quality parameters affecting the bioavailability of metals, where the concentration of bioavailable is determined by the use of appropriate bioavailability model.
9. MKE Biota: European environmental quality requirement for water for biota, expressed in unit [ μg/kg wet weight]
10. date of realisation of the environmental quality requirement for water for the priority substance: 22 December 2015 (for the relevant substance identified by X)
11. date of realisation of the environmental quality requirement for water for the priority substance: 22 December 2021 (for the relevant substance identified by X)
12. date of realization of the environmental quality requirement for water for the priority substance: 22 December 2027 (for the relevant substance identified by X)
1
2
3
4
5
6
7
8
9
10
11
12
No
CAS number (1)
EU number (2)
Name of the priority substance
(X) = also designated as a priority hazardous substance
JG-MKE
Area of land area (3)
JG-MKE
Other area waters (3)
MAC MKE
Area of land area (3)
MAC MKE
Other area waters (3)
MKE
Biota
2015
2021
2027
| 1 |
15972-60-8 |
240-110-8 |
Alachlor |
0.3 |
0.3 |
0.7 |
0.7 |
X |
|||
| 2 |
120-12-7 |
204-371-1 |
Anthracone (X) |
0.1 |
0.1 |
0.4 |
0.4 |
X |
|||
| 0.1 |
0.1 |
0.1 |
0.1 |
X |
|||||||
| 3 |
1912-24-9 |
217-617-8 |
Atrazine |
0.6 |
0.6 |
2.0 |
2.0 |
X |
|||
| 4 |
71-43-2 |
200-753-7 |
Benzene |
10 |
8 |
50 |
50 |
X |
|||
| 5 |
32534-81-9 |
Brominated diphenylethers (5) (X) (4) |
0.0005 |
0.0002 |
N/A |
N/A |
X |
||||
| 0.14 |
0.014 |
0.0085 |
X |
||||||||
| 6 |
7440-43-9 |
231-152-8 |
Cadmium and cadmium compounds (depending on the water hardness class) (6) (X) |
≤ 0,08 (Class 1) 0.08 (Class 2) 0,09 (Class 3) 0,15 (Class 4) 0,25 (Class 5) |
0.2 |
≤ 0,45 (Class 1) 0.45 (Class 2) 0.6 (Class 3) 0.9 (Class 4) 1.5 (Class 5) |
≤ 0,45 (Class 1) 0.45 (Class 2) 0.6 (Class 3) 0.9 (Class 4) 1.5 (Class 5) |
X |
|||
| 6a |
56-23-5 |
Carbon tetrachloride (7) |
12 |
12 |
N/A |
N/A |
X |
||||
| 7 |
85535-84-8 |
287-476-5 |
C-1013-Chloralkanes (8) (X) |
0.4 |
0.4 |
1.4 |
1.4 |
X |
|||
| 8 |
470-90-6 |
207-432-0 |
Chlorfenvinphos |
0.1 |
0.1 |
0.3 |
0.3 |
X |
|||
| 9 |
2921-88-2 |
220-864-4 |
Chloryriphos (Chlorpyrifos-ethyl) |
0.03 |
0.03 |
0.1 |
0.1 |
X |
|||
| 9a |
309-00-2 60-57-1 72-20-8 465-73-6 |
Cyclodione pesticides: Aldrin (7) Dieldrin (7) Endrin (7) Isodrin (7) |
Σ = 0,01 |
Σ = 0,005 |
N/A |
N/A |
X |
||||
| 9b |
N/A |
Total DDT (7) (9) |
0.025 |
0.025 |
N/A |
N/A |
X |
||||
| 9b |
50-29-3 |
para-para-DDT (7) |
0,01 |
0,01 |
N/A |
N/A |
X |
||||
| 10 |
107-06-2 |
203-458-1 |
1,2-dichloroethane |
10 |
10 |
N/A |
N/A |
X |
|||
| 11 |
75-09-2 |
200-838-9 |
Dichloromethane |
20 |
20 |
N/A |
N/A |
X |
|||
| 12 |
117-81-7 |
204-211-0 |
Di (2-ethylhexyl) phthalate (DEHP) (X) (19) |
1.3 |
1.3 |
N/A |
N/A |
X |
|||
| 13 |
330-54-1 |
206-354-4 |
Diuron |
0.2 |
0.2 |
1.8 |
1.8 |
X |
|||
| 14 |
115-29-7 |
204-079-4 |
Endosulfan (X) |
0.005 |
0.0005 |
0,01 |
0.004 |
X |
|||
| 15 |
206-44-0 |
205-912-4 |
Fluorantan |
0.1 |
0.1 |
1 |
1 |
X |
|||
| 0.0063 |
0.0063 |
0.12 |
0.12 |
30 |
X |
||||||
| 16 |
118-74-1 |
204-273-9 |
Hexachlorobenzene (X) |
0.000026 (21) |
0.000026 (21) |
0.05 |
0.05 |
10 |
X |
||
| 17 |
87-68-3 |
201-765-5 |
Hexachlorobutadiene (X) |
0.00055 (21) |
0.00055 (21) |
0.6 |
0.6 |
55 |
X |
||
| 18 |
608-73-1 |
210-158-9 |
Hexachlorocyclohexane (X) |
0.02 |
0.002 |
0.04 |
0.02 |
X |
|||
| 19 |
34123-59-6 |
251-835-4 |
Isoproturon |
0.3 |
0.3 |
1.0 |
1.0 |
X |
|||
| 20 |
7439-92-1 |
231-100-4 |
Lead and lead compounds |
7.2 |
7.2 |
N/A |
N/A |
X |
|||
| 1.2 (13 ) |
1.3 |
14 |
14 |
X |
|||||||
| 21 |
7439-97-6 |
231-106-7 |
Mercury and Mercury Compounds (X) |
0.0007 (21) |
0.0007 (21) |
0.07 |
0.07 |
20 |
X |
||
| 22 |
91-20-3 |
202-049-5 |
Naphthalenes |
2.4 |
1.2 |
N/A |
N/A |
X |
|||
| 2 |
2 |
130 |
130 |
X |
|||||||
| 23 |
7440-02-0 |
231-111-14 |
Nickel and nickel compounds |
20 |
20 |
N/A |
N/A |
X |
|||
| 4 (13) |
8.6 |
34 |
34 |
X |
|||||||
| 24 |
84852-15-3 |
N/A |
Nonylphenols (X) (22) |
0.3 |
0.3 |
2.0 |
2.0 |
X |
|||
| 25 |
104-66-9 |
N/A |
Octylphenols (4-(1,1 ', 3,3'-tetramethylbutyl)-phenol) (15) |
0.1 |
0,01 |
N/A |
N/A |
X |
|||
| 26 |
608-93-5 |
210-172-0 |
Pentachlorobenzene (X) |
0.007 |
0.0007 |
N/A |
N/A |
X |
|||
| 27 |
87-86-5 |
231-152-8 |
Pentachlorophenol |
0.4 |
0.4 |
1 |
1 |
X |
|||
| 28 |
N/A |
N/A |
Polycyclic aromatic hydrocarbons (PAH) (11) (16) (X) |
N/A |
N/A |
N/A |
N/A |
X |
|||
| 28 |
50-32-8 |
Benzo (a) pyrene (X) |
1,7 × 10 -4 |
1,7 × 10 -4 |
0.27 |
0.027 |
5 |
X |
|||
| 28 |
205-99-2 |
Benzo (b) fluorantone (X) |
(11) |
(11) |
0.017 |
0.017 |
(11) |
X |
|||
| 28 |
207-08-9 |
Benzo (k) fluorantone (X) |
(11) |
(11) |
0.017 |
0.017 |
(11) |
X |
|||
| 28 |
191-24-2 |
Benzo (g, h, i)-perylene (X) |
(11) |
(11) |
8,2 × 10 -3 |
8,2 × 10 -4 |
(11) |
X |
|||
| 28 |
193-39-5 |
Indeno (1,2,3-cd) pyrene (X) |
(11) |
(11) |
N/A |
N/A |
(11) |
X |
|||
| 29 |
122-34-9 |
204-535-2 |
Simazine |
1 |
1 |
4 |
4 |
X |
|||
| 29a |
127-18-4 |
Tetrachloroethylene (7) |
10 |
10 |
N/A |
N/A |
X |
||||
| 29b |
79-01-6 |
79-01-6 |
Trichloroethylene (7) |
10 |
10 |
N/A |
N/A |
X |
|||
| 30 |
36643-28-4 |
N/A |
Tributyltin compounds (X) (17) |
0.0002 |
0.0002 |
0.0015 |
0.0015 |
X |
|||
| 31 |
12002-48-1 |
234-413-4 |
Trichlorobenzene |
0.4 |
0.4 |
N/A |
N/A |
X |
|||
| 32 |
67-66-3 |
200-663-8 |
Trichloromethane (chloroform) |
2.5 2.5 |
2.5 2.5 |
N/A |
N/A |
X |
|||
| 33 |
1582-09-8 |
216-428-8 |
Trifluralin (X) (19) |
0.03 |
0.03 |
N/A |
N/A |
X |
|||
| 34 |
115-32-2 |
204-082-0 |
Dicofol (X) (19) |
1.3 10 -3 |
3.2 10 -5 |
N/A (10) |
N/A (10) |
33 |
X |
||
| 35 |
1763-23-1 |
217-179-8 |
Perfluorooctane sulfonic acid and its derivatives (PFOS) (X) (19) |
6.5 10 -4 |
1.3 10 -4 |
36 |
7.2 |
9.1 |
X |
||
| 36 |
124495-18-7 |
N/A |
Quinoxyfen (X) (19) |
0,15 |
0.015 |
2.7 |
0.54 |
X |
|||
| 37 |
(18) |
N/A |
Dioxins and dioxin-like compounds (X) |
N/A |
N/A |
Sum of PCDD + PCDF + PCB-DL 0,0065 μg.kg -1 TEQ (14) |
X |
||||
| 38 |
74070-46-5 |
277-704-1 |
Aclonifen |
0.12 |
0.012 |
0.12 |
0.012 |
X |
|||
| 39 |
42576-02-3 |
255-894-7 |
Bifenox |
0.012 |
0.0012 |
0.04 |
0.004 |
X |
|||
| 40 |
28159-98-0 |
248-872-3 |
Cybutryne |
0.0025 |
0.0025 |
0.016 |
0.016 |
X |
|||
| 41 |
52315-07-8 |
257-842-9 |
Cypermethrin (23) |
8 10 -5 |
8 10 -6 |
6 10 -4 |
6 10 -5 |
X |
|||
| 42 |
62-73-7 |
200-547-7 |
Dichlorvos |
6 10 -4 |
6 10 -5 |
7 10 -4 |
7 10 -5 |
X |
|||
| 43 |
N/A |
Hexabromocyclododecane (HBCDD) (X (19) ) (20) |
0.0016 |
0.0008 |
0.5 |
0.05 |
167 |
X |
|||
| 44 |
CAS No 76-44-8/1024-57-3 |
200-962-3/213-831-0 |
Heptachlor and heptachlor-poxide (X (19) ) |
2 10 -7 |
1 10 -8 |
3 10 -4 |
3 10 -5 |
6.7 10 -3 |
X |
||
| 45 |
886-50-0 |
212-950-5 |
Terbutryn |
0.065 |
0.0065 |
0.34 |
0.034 |
X |
(1) CAS: Chemical Abstract Services.
(2) EU number: European Inventory of Existing Commercial Chemical Substances (EINECS) or the European List of Chemical Substances notified (ELINCS).
(3) Land surface waters include rivers and lakes and the associated artificial or highly altered water bodies.
Other surface waters include coastal and transitional waters, including derived artificial and heavily altered water bodies.
(4) Only tetra-, penta-, hexa-and heptabromodiphenyl ether (CAS numbers 40088-47-9, 32534-81-9, 36483-60-0, 68928-80-3).
(5) For the group of priority substances covered by brominated diphenyl ethers (No 5) refers the MKE to the sum of the concentrations for the congeners. 28, 47, 99, 100, 153, and 154.
(6) For cadmium and its compounds ( 6) the JG-MKE and MAC-MKE concern the dissolved concentrations and the MKE values are dependent on the hardness of the water, classified in five classes (class 1: < 40 mg CaCO3 /l, class 2: 40 to < 50 mg CaCO3 /l, class 3: 50 to < 100 mg) CaCO3 /l, class 4: 100 to < 200 mg CaCO3 /l and class 5: ≥ 200 mg CaCO3 /l).
(7) This substance is not a priority substance, but one of the other pollutants for which the MKN are identical to those laid down in the legislation applicable before 13 January 2009.
(8) No indicative parameter is specified for this group of substances. The indicative parameters should be determined by the analytical methods.
(9) DDT total consists of the sum of isomers 1,1,1-trichloro-2,2-bis (p-chlorophenyl) ethane (CAS number 50-29-3), EU number 200-024-3); 1,1,1-trichloro-2-(o-chlorophenyl) -2-(p-chlorophenyl) ethane (CAS number 789-02-6); EU number 212-332-5); 1,1-dichlorom2,2- bis (p-chlorophenyl) ethylene (CAS number 72-55-9); EU number 200-784-6); and 1,1-dichloro-2,2-bis (p-chlorophenyl) ethane (CAS number 72-54-8); EU number 200-783-0).
(10) Insufficient information is available to establish a MAC-MKE for these substances.
(11) For the group of priority substances subject to polycyclic aromatic hydrocarbons (PAH), the mentioned biota-MKE and corresponding JG-MKE for water is the concentration of benzo (a) pyreen; both MKE are on the toxicity of benzo (a) pyrene based. Benzo (a) pyrene can be considered as a marker for other PAH and therefore the monitoring of benzo (a) pyrene for the biota-MKE and the corresponding JG-MKE should be monitored.
(12) Unless otherwise specified, the biota-MKE shall apply to fish. Alternatively, an alternative biotataxone or any other matrix may be monitored to the extent that the applied MKE provides an equivalent level of protection. For the substances with number 15 (fluorantheen) and 28 (PAH), the biota-MKE shall apply to shellfish and molluscs. For the assessment of the chemical status, the monitoring of fluorantan and PAH in fish is not appropriate. For dust number 37 (dioxins and dioxin-like compounds), the biota-MKE shall apply to fish, shellfish and molluscs; see Section 5.3 of the Annex to Regulation (EU) No 248/ (2). Commission Regulation (EC) No 1259/2011 of 2 December 2011 amending Regulation (EC) No 1259/2011 EUR 1881/2006 as regards the maximum levels for dioxins, dioxin-like PCBs and non-dioxin-like PCBs in foodstuffs (OJ L 320, 3.12.2011, p. 18).
(13) These EQS refer to the biologically available concentrations of the substances.
(14) PCDDs: polychlorinated dibenzo-p-dioxins; PCDFs: polychlorinated dibenzofurans; PCB DL: dioxin-like polychlorinated biphenyls; TEQs: toxic equivalents, according to World Health Organisation Toxic Equivalency Factors (2005).
(15) Octylphenol (CAS 1806-26-4, EU 217-302-5) including isomer 4-(1,1 ', 3,3'-tetramethylbutyl)-phenol (CAS 140-66-9, EU 205-426-2).
(16) Including benzo (a) pyrene (CAS 50-32-8, EU 200-028-5), benzo (b) fluorantene (CAS 205-99-2, EU 205-911-9), benzo (g, h, i) perylene (CAS 191-24-2, EU 205-883-8), benzo (k) fluorantene (CAS 207-08-9, EU 205-916-6), indeno (1,2,3-cd) pyrene (CAS 193-39-5, EU) 205-893-2) and except for anthracen, fluorantane-one and naphthalenes, which are listed separately.
(17) Including tributyltin kation (CAS 36643-28-4).
(18) These are the following compounds: 7 polychlorinated dibenzo-p-dioxins (PCDDs): 2,3,7,8-T4CDD (CAS 1746-01-6), 1,2,3,7,8-P5CDD (CAS 40321-76-4), 1,2,3,4,7,8-H6CDD (CAS 39227-28-6), 1,2,3,6,7,8-H6CDD (CAS 57653-85-7), 1,2,3,7,8,9-H6CDD (CAS 19408-74-3), 1,2,3,4,6,7,8-H7CDD (CAS 35822-46-9), 1,2,3,4,6,7,8,9-O8CDD (CAS 3268-87-9) 10 polychlorodibenzofurans (PCDFs): 2,3,7,8-T4CDF (CAS 51207-31-9), 1,2,3,7,8-P5CDF (CAS 57117-41-6), 2,3,4,7,8-P5CDF (CAS 57117-31-4), 1,2,3,4,7,8-H6CDF (CAS 70648-26-9), 1,2,3,6,7,8-H6CDF (CAS 57117-44-9), 1,2,3,7,8,9-H6CDF (CAS) (CAS 52918-21-9), 2,3,4,6,7,8-H6CDF (CAS 60851-34-5), 1,2,3,4,6,7,8-H7CDF (CAS 67562-39-4), 1,2,3,4,7,8,9-H7CDF (CAS 55673-89-7), 1,2,3,4,6,7,8,9-O8CDF (CAS 39001-02-0) 12 dioxin-like polychlorinated biphenyls (DL-PCB): 3,3 ', 4,4' -T4CB (PCB 77, CAS 32598-13-3), 3.3 ', 4', 5-T4CB (PCB 81, CAS 70362-50-4), 2,3,3 ', 4,4' -P5CB (PCB 105, CAS 32598-14-4), 2,3,4,4 ', 5-P5CB (PCB 114, CAS 74472-37-0), 2,3', 4,4 ', 5-P5CB (PCB 118, CAS 31508-00-6), 2,3', 4,4 ', 5' -P5CB (PCB 123, CAS 65510-44-3), 3,3 ', 4,4', 5-P5CB (PCB 126, CAS). 57465-28-8), 2,3,3 ', 4,4', 5-H6CB (PCB 156, CAS 38380-08-4), 2,3,3 ', 4,4', 5 '-H6CB (PCB 157, CAS 69782-90-7), 2,3', 4,4 ', 5,5' -H6CB (PCB 167, CAS 52663 72-6), 3,3 ', 4,4', 5,5 '-H6CB (PCB 169, CAS 32774-16-6), 2,3,3', 4,4 ', 5,5' -H7CB (PCB 189, CAS 39635-31-9).
(19) These substances were first designated as a priority hazardous priority substance as of 22 December 2015.
(20) These are 1,3,5,7,9,11-hexabromocyclododecane (CAS 25637-99-4), 1,2,5,6,9,10-hexabromocyclododecane (CAS 3194-55-6), α-hexabromocyclododecane (CAS 134237-50-6), β-hexabromocyclododecane (CAS 134237-51-7) and γ-hexabromocyclododecane (CAS 134237-52-8).
(21) For this substance, the Netherlands has for the purpose of monitoring compliance with the environmental quality requirement for biota, having regard to Article 3, third paragraph, of the Directive priority substances, a value for the concentration of the substance in surface water derived, providing the same level of protection that is envisaged with the environmental quality requirement for biota. For mercury and its compounds (21), the JG-MKE and MAC-MKE refer to the dissolved concentrations. No adjustment for the natural background concentration shall be applied to the JG-MKE listed in the table.
(22) Nonylphenol (CAS 25154-52-3, EU 246-672-0) including isomers 4-nonylphenol (CAS 104-40-5, EU 203-199-4) and 4-nonylphenol (branched) (CAS 84852-15 -3, EU 284-325-5).
(23) CAS 52315 -07-8 concerns a mixture of isomers of cypermethrin, alpha-cypermethrin (CAS 67375-30-8), beta-cypermethrin (CAS 65731-84-2), theta-cypermethrin (CAS 71697-59-1) and zeta-cypermethrin (52315 -07-8).
The following European environmental quality requirements for water refer to groundwater bodies. They have been adopted to implement the groundwater quality standards set out in Annex I to the groundwater directive.
Pollutant
European environmental quality for water
| Nitrates |
50 mg/l |
| Active substances in plant protection products, including their relevant conversion, breakdown and reaction products thereof 1 |
0,1 μg/l 0.5 μg/l (total) 2 |
The following European environmental quality requirements for water refer to groundwater bodies. They have been established by the Netherlands as thresholds for implementation of Article 3 (b) and (sixth) of the groundwater directive, taking into account Annex VIII to the Water Framework Directive, having regard to the guidelines, referred to in Annex II, Part A, to that Directive and taking into account the minimum lists provided for in Part B of that Annex.
Groundwater bodies
European environmental quality requirements for water for pollutants
Code
Description
Type
Cl mg/l
Ni μg/l
Axle μg/l
Cd μg/l
Pb μg/l
P-to mg/l
| NLGW0001 |
Sand Ems |
Sand |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0008 |
Salt Ems |
Salt |
Brak&salt |
20 |
18.7 |
0.35 |
7.4 |
6.9 |
|
| NLGW0002 |
Sand Rhine-North |
Sand |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0007 |
Salt Rhine-North |
Salt |
Brak&salt |
20 |
18.7 |
0.35 |
7.4 |
6.9 |
|
| NLGW0009 |
Coat Rhine-North |
Coating |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0015 |
Wadden Rhine-North |
Dune |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0004 |
Sand Rhine-Middle |
Sand |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0003 |
Sand Rhine-East |
Sand |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0010 |
Coat Rhine-East |
Coating |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0005 |
Sand Rhine-West |
Sand |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0011 |
Salt Rhine-West |
Salt |
Brak&salt |
20 |
18.7 |
0.35 |
7.4 |
6.9 |
|
| NLGW0012 |
Coat Rhine-West |
Coating |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0016 |
Duin Rhine-West |
Dune |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0006 |
Sand Meuse |
Sand |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0013 |
Salt Meuse |
Salt |
Brak&salt |
20 |
18.7 |
0.35 |
7.4 |
6.9 |
|
| NLGW0017 |
Duin Maas |
Dune |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGW0018 |
Maas-Slenk-deep |
N/A |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
|
| NLGW0019 |
Chalk South Limburg |
N/A |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGWSC0001 |
Fresh groundwater dune areas |
Dune |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGWSC0002 |
Fresh groundwater decksand |
Sand |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGWSC0003 |
Fresh groundwater creek areas |
N/A |
Sweet |
160 |
20 |
13.2 |
0.35 |
7.4 |
2.0 |
| NLGWSC0004 |
Salt groundwater in shallow sand layers |
Salt |
Brak&salt |
20 |
18.7 |
0.35 |
7.4 |
6.9 |
|
| NLGWSC0005 |
Groundwater deep sand layers |
N/A |
Brak&salt |
20 |
18.7 |
0.35 |
7.4 |
The following European environmental quality requirements for water refer to surface water used in the preparation of water intended for human consumption.
Parameter
European Environment Quality Water for Water
Unit
Tree nuts
| Acidity |
7,0-9,0 |
pH |
|
| Color intensity |
50 |
mg/1 |
|
| Suspended solids |
50 |
mg/1 |
|
| Temperature |
25 |
° C |
|
| Conductivity for electricity |
80 |
mS/m at 20 °C |
|
| Chloride |
150 |
Mg/l Cl |
|
| Sulphate |
100 |
mg/l SO4 |
|
| Fluoride |
1 |
mg/l F |
|
| Ammonium |
1.5 |
mg/l NH4 |
|
| Nitrate |
50 |
mg/l NO3 |
|
| Phosphate |
0.9 |
mg/l PO4 |
|
| Dissolved Oxygen |
≥ 5 |
Mg/l O2 |
|
| Sodium |
120 |
mg/1 |
|
| Iron Dissolved |
0.3 |
mg/1 |
|
| Mangled |
500 |
μg/l |
|
| Copper |
50 |
μg/l |
|
| Zinc |
200 |
μg/l |
|
| Boron |
1.000 |
μg/l |
|
| Arsenic |
20 |
μg/l |
|
| Cadmium |
1.5 |
μg/l |
|
| Chromium (total) |
20 |
μg/l |
|
| Lead |
30 |
μg/l |
|
| Selenes |
10 |
μg/l |
|
| Mercury |
0.3 |
μg/l |
|
| Barium |
200 |
μg/l |
|
| Cyanide |
50 |
μg/l CN |
|
| Polycyclic aromatic hydrocarbons |
1 |
μg/l |
1 |
| Plant protection products, biocides and their humiditoxicologically relevant degradation products per individual substance |
0.1 |
μg/l |
1, 2 |
| Bacteria of the coligroup (total) |
2.000 |
Number per 100 ml |
|
| Escherichia coli |
2.000 |
Number per 100 ml |
|
| Enterococci |
1.000 |
Number per 100 ml |
1. For this group parameter, the monitoring programme shall specify which substances are to be measured.
2. For degradation products of plant protection products and biocides, a distinction is made on the basis of skin toxicological relevance. The European environmental quality requirement for water of 0,1 μg/l shall only apply to weeping toxicologically relevant degradation products.
