Appendix 1	Analyzing the characteristics of the river basin district and evaluation of the impact of human activity on the status of the surface water and the groundwater
Appendix 2	Financial analysis of water use

Publication of basic analysis 1)

In accordance with section 6 (4), 2, in the environmental dimensions and in the case of water bodies and international natural protection areas (environmental target sloven), cf. Law Order no. 932 of 24. September 2009, and section 6 (4). Three, in the law. 1606 of 26. December 2013 on water planning shall be determined according to the authorization referred to in section 2 (2). 1, in the notice. 973 of 29. August 2014 on the execution of tasks and powers to the natural authority :

§ 1. This notice lays down rules for :

1) analysis of the characteristics of the river basin district,

2) assessments of the impact of human activity on the status of the surface water and the groundwater ; and

3) financial analysis of water use.

§ 2. The nature management shall identify the location and boundaries of surface waters within river basin districts.

Paragraph 2. The steering shall characterize and type in surface water areas, in accordance with the procedure laid down in Annex 1, Part A, section 1, and in accordance with the specifications referred to in Part A's section 3.

Paragraph 3. The steering shall determine type-specific or river basin management specific reference conditions for the individual types of surface water areas in accordance with the procedure laid down in Annex 1, Part A, section 4.

§ 3. The nature of the natural authority identifies significant man-made workloads of surface waters in accordance with the specifications set out in Part A of Annex 1 (5) and assess the impact thereof on the condition of the surface water in accordance with the procedures mentioned in Part A's section 6.

§ 4. The National Wildlife Agency identifies the location and boundaries of groundwater bodies in river basin districts.

Paragraph 2. The steering is characterizing and assessing the groundwater instances in accordance with the specifications in Annex 1, Part B, section 1.

§ 5. The nature of the natural authority shall characterize further the groundwater bodies which, according to the risk assessment in Annex 1, Part B, are not expected to be able to meet the environmental objectives. The additional characterization shall be made in accordance with Annex 1, Part B, section 2.

Paragraph 2. The steering assesses the impact of human activities on groundwater bodies crossing the Danish-German border on the basis of information gathered in accordance with Annex 1, Part B, Section 3. The same applies to groundwater bodies which, according to the risk assessment in Annex 1, Part B, are not expected to be able to meet the environmental objectives.

§ 6. The Natural Management Board shall draw up an overview of emissions, discharges and losses of substances covered by Part C of Annex 2 to the publication of the environmental objectives for watercourses, lakes, transitional waters, coastal waters and ground water, including : concentrations of substances in sediments and biota. In the view, a card shall be made available if such are available.

Paragraph 2. The view of paragraph 1. 1 shall be prepared on the basis of information collected according to section 3 to 5, through the surveillance referred to in section 31 (3). 1, in the law on water planning and in accordance with Council Regulation (EEC) 166/2006 by 18. January 2006 establishing a European register of discharges and the transfer of pollutants and amending Council Directive 91 /61/EC and other information available.

Paragraph 3. The view of paragraph 1. 1 shall be updated as part of the review and updating of the basic assessment in accordance with section 6 (4). Two, in the law of water planning.

Paragraph 4. As a reference period for the assessment of emissions, discharges and losses in the updated summaries, the last year shall be used before the relevant basic analysis must be drawn up. For priority substances and pollutants covered by Regulation (EC) No 1107/2009 of the European Parliament and of the Council of 21. In October 2009, on the placing of plant protection products on the market and repealing Council Directive 79 /117/EEC and 91 /414/EEC, emissions, discharges and losses shall be achieved as the average for the last three years prior to the basic analysis.

§ 7. The FDA shall carry out an economic analysis of water use in river basin districts, in accordance with the specifications set out in Annex 2.

§ 8. The announcement will enter into force on the 19th. December 2014.

Paragraph 2. The following notices shall be deleted :

1) Publication no. 1355 of 11. December 2006 on the characterisation of water deposits, the imposition of influences and the mapping of water resources in subsequent amendments are repealed.

2) Publication no. 39 of 19. January, 2011, on the preparation of economic analysis for the use of water plans shall be repealed.

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Appendix 1

Analyzing the characteristics of the river basin district and evaluation of the impact of human activity on the status of the surface water and the groundwater

Part A. Surface water.

1. Characteristics of surface water bodies

The nature and nature of the natural body shall identify the location and boundaries of the surface waters and make a first characterisation of such waters in accordance with the following procedure. The nature of the natural authority may group surface water bodies for the purposes of this first characterisation.

1) surface water areas in the river basin district are characterized as belonging to a surface river basin area, sea, sea, transitional waters and coastal waters or as artificial surface water areas or heavily modified surface water areas.

2) For each category of surface water, the relevant surface waters of the river basin district shall be divided according to the type, as defined by using either system A or System B as described in Section 2.

3) Benyttes System A, divide surface water bodies into the river basin district shall only, in accordance with the geographical areas referred to in section 2 and shown on the relevant card in section 2.5, shall be divided into the river basin district. The surface water areas in each ecoregion shall then be divided into types of water areas after the descriptors in the tables under system A.

4) Benytte's system B shall mean the same level of division as the one that would have been obtained with the system A ; in other terms, the surface waters of the river basin district are broken down into types using the values of the mandatory descriptors and in the case of such optional descriptors, or combinations of descriptors necessary to ensure that type-specific biological reference conditions may be derived with the necessary reliability.

5) Artificial or heavily modified surface water bodies shall be broken down according to the descriptors of the surface river basin management category that most resemdices the highly modified or artificial water area.

6) One or more maps shall be drawn up in GIS format showing the geographical location of the bulls corresponding to the level of division required under system A.

2. Ocoregions and types of surface water bodies

2.1. Water Run

System A

System B

2.2. Searching

System A

System B

2.3. Transitional waters

System A

System B

2.4. Coastal waters

System A

System B

2.5. Maps

System A. Ecoregions for watercourses and lakes

Short A

System A : Ecoregions for transitional waters and coastal waters

Short B

3. type-sharing of surface water bodies

3.1. Type-sharing of water flows

The type-distribution of water flows or water-flow lines shall be done in accordance with System B in section 2.1, as indicated in the following table.

Type-sharing of water flow.

3.2. Type partitioning of lakes

The type-distribution of lakes shall take place in accordance with System B in section 2.2 as indicated in the following table.

Type-partitioning of sweees.

3.3. Type-sharing of transitional waters and coastal waters

The type-sharing of transitional waters and coastal waters shall be done in accordance with the system B in sections 2.3 and 2.4, as shown in the following tables.

The type-sharing of open coastal waters and the overview of water areas.

Type partitioning of fjords and closed coastal waters.

Overview of the fjords and closed coastal waters.

4. Establishment of type-specific reference conditions for the types of surface water bodies

Type-specific or river basin management specific reference conditions for the types of surface waters shall be determined in accordance with the following procedures.

1) For each type of surface water characteristic characterized in accordance with Title 1, type-specific hydromorphological and physico-chemical ratio corresponding to the values of the values referred to in section 1 of Annex 3 to the Notice on Monitoring of the state of surface water, groundwater and protected areas and on night monitoring of international natural protection areas listed hydromorphological and physico-chemical quality elements for the type of surface water surface area ; the ecological status as defined in the relevant section of Annex 1 to : publication of the environmental objectives for watercourses, lakes, transitional waters, coastal waters and ground water. Type-specific biological reference ratio corresponding to the values of the conditions laid down in section 1 of Annex 3 relating to the surveillance of the state of surface water, groundwater and protected areas, and on night monitoring of international international law ; in the case of natural protection, biological quality elements specified for the type of surface water in the area concerned, as defined in Annex 1 in the relevant section of Annex 1 to the establishment of environmental objectives for water, lakes, Transitional waters, coastal waters and ground water.

2) In the case of large variation in a type of surface water species characterized in accordance with Section 1, non-conformity-specific reference conditions may be used for specific biological quality elements rather than those of the the type-specific reference conditions referred to in paragraph 1 shall be laid down for the river basin-basin-specific reference conditions where, for the surface waters concerned, representative historical observations of the quality element in question are available for high ecologically ; state, or the reference conditions for those concerned, surface waters may be derived by means of models, cf. Paragraph 6.

3) Where the procedures described in this section are used on artificial or heavily modified surface waters, references to high ecological status shall be construed as references to maximum ecological potential as defined in Section 6 ; in Annex 1 to the publication on the establishment of environmental objectives for watercourses, lakes, transitional waters, coastal waters and ground water. The values of the maximum ecological potential of an aquatic area are reviewed every six years.

4) The type-specific hydromorphological and physical-chemical conditions referred to in points 1 and 3 and the type-specific biological reference conditions can be based on either spacing or models, or may be deducated from a combination of these methods. When these methods are not available, expert opinion may be used to determine such conditions. In the definition of high ecological status as regards the concentration of certain synthetic pollutants, the limit of detection is the one that can be achieved by means of available technology at the time of the type-specific conditions ; establishes.

5) For type-specific biological reference conditions based on spacer, a reference centre for each type of surface water shall be set up. The network must contain sufficient reference points of high state to ensure that the reference conditions are sufficiently credible in view of the variability of the values of the quality elements corresponding to high state of : the type of surface water concerned, and in the light of the modeling techniques to be used in accordance with section 6.

6) Model-based type-specific or river basin-specific biological reference conditions can be derived using either forecast models or write-back methods. The methods must include the use of historical, paleological and other data available, and shall ensure that the reference conditions are sufficiently credible to ensure that the conditions thus derived are compatible and valid ; for each type of surface water or of the surface water bodies concerned.

7) When it is not possible to establish reliable type-specific or river basin-specific reference conditions for a quality element in a type of surface water area because of the high natural variability of the element, which is not only due to seasonal nature ; variations, may the element in question be omitted from the assessment of the ecological status of the surface water type concerned.

5. Workloads Identification

The National Agency shall collect and store information on the type and scale of the significant man-made workloads to which surface waters of the river basin district will be exposed. Such information shall include in particular :

-WHAT? Assessment and identification of significant point source contamination, in particular with substances referred to in Part A, section 1 of Annex 2, to the publication of the environmental objectives for water flows, lakes, transitional waters, coastal waters and ground water, biocides and plant protection products, towed substances, substances which contribute to eutrophication and substances which have a negative impact on the oxygen balance, from urban, industrial and agricultural installations and other installations and activities, based, inter alia, on information collected in following :

-WHAT? the supervision of discharges from point sources, cf. section 65-66 in the law of environmental protection,

-WHAT? the drawing up of records in accordance with section 52 of the waste water licences and so on in accordance with Chapters 3 and 4 of the environmental protection law,

-WHAT? the announcement of the approval of the list company, section 6, section 9, section 11, sections 13 and § § 42-43,

-WHAT? the permit and approval etc. of livestock farming § § 6-8, § § § -16, § 20, § 41, § 47, § 50, and § 55, and

-WHAT? notification of certain air polluting emissions from combustion plants on platforms at sea § § 4 and 5.

-WHAT? Assessment and identification of significant pollution from diffuse sources, in particular with substances referred to in Part A, section 1 of Annex 2 to the publication of the environmental objectives for watercourses, lakes, transitional waters, coastal waters and ground water, biocides, and plant protection products, towed substances, substances which contribute to eutrophication and substances which have a negative impact on the oxygen balance, from urban, industrial and agricultural installations and other installations and activities, based on information collected, inter alia, following :

-WHAT? Annex 1, Section 4.2, and Annex 2, Section 5, in the notice on the monitoring of the state of surface water, groundwater and protected areas, and the night-awakening of international nature conservation areas ;

-WHAT? Articles 56 and 68 of Regulation (EC) No, of the European Parliament and of the Council 1107/2009 of 21. Oct 2009 on the placing of plant protection products on the market and repealing Council Directive 79 /117/EEC and 91 /414/EEC, and

-WHAT? Regulation (EC) No 2 of the European Parliament and of 528/2012 of 22. May 2012 on the availability of goods on the market and the use of biocidal products.

-WHAT? Assessment and identification of significant abstraction of water for urban, industrial and agricultural purposes and other purposes, including seasonal variations and annual demand and water losses in the supply networks.

-WHAT? Assessment and identification of the effects of significant water flow regulation, including water transfer and rewire, on the flow characteristics and the water balance as a whole.

-WHAT? Identification of significant morphological changes in water areas.

-WHAT? Assessment and identification of other significant man-made influences of surface water status.

-WHAT? Assessment of area use patterns, including identification of the main urban, industrial and agricultural areas and, where applicable, fishing and forests.

6. Environmental impact assessment

The Board of Natural Board assesses the impact of the surface waters in the light of the abode mentioned above.

The Services Management Board shall make use of the information gathered above and all other relevant information including environmental surveillance data, to assess the likelihood of surface water bodies in the river basin district to meet the environmental objectives ; in section 7 (4). 2, no. Two, in the law of water planning. Member States may use models of modeling such as the support of such an assessment.

In the case of review and updating of basic analysis, the forecast probability assessment shall cover the likelihood that surface water bodies in the river basin district cannot fulfil the target of good surface water conditions or, for artificial and strong, modified waters, good ecological potential and good chemical status for surface waters at the end of the subsequent schedule.

Water areas considered to be unable to meet the environmental objectives, where appropriate, shall be further characterized to optimize the design of both the monitoring programmes to be drawn up in accordance with section 31 (3). 2, in the area of water planning, and the intervention programme shall be fixed in section 19 (1). One, in the same law.

Part B. Groundwater.

1. First characterisation of groundwater

There is a first characterisation of all groundwater in order to assess its use and the risk that it does not meet the objectives set out in section 7 (2). 2, no. Two, in the law of water planning. For the purposes of this first characterisation, groundwater bodies can be assembled in groups. In this analysis, existing hydrological, geological and pedo data and data on land use, derivation, abstraction, abstraction and other data may be used, but the following shall be mapped :

-WHAT? the location and limits of the groundwater body or occurrences,

-WHAT? the strain that the groundwater body or instances are likely to be subjected to, from among other things,

-WHAT? diffuse sources of pollution,

-WHAT? point sources of pollution,

-WHAT? abstraction and

-WHAT? artificial infiltration,

-WHAT? the nature of the overlying layers of the basic water-forming area from which the groundwater body is brought to water,

-WHAT? the groundwater bodies for which direct dependent surface water ecosystems or terrestrial ecosystems are.

In the case of review and updating of basic analysis, the above risk assessment shall cover the risk that groundwater bodies in the river basin district cannot fulfil the objective of good groundwater status at the end of the subsequent schedule period.

2. Additional characterisation of groundwater

After the first characterisation, further characterisation of the groundwater bodies or groups of groundwater bodies deemed to be threatened so that the extent of the risk can be assessed more accurately and in such a way that it is ; it may be possible to identify the measures to be determined in the work programme with the home meal in section 19 (3). One, in the law of water planning. This characterisation must therefore include relevant information on the impact of the human activity and, where appropriate, information on :

-WHAT? geological characteristics of the groundwater body, including the extent and type of geological units and types of geological units ;

-WHAT? hydrogeological characteristics of the groundwater body, including hydraulic conductivity, porosity and climatics,

-WHAT? the characteristics of surface deposits and soil in the ground water forming area from which the groundwater body is added to water, including their thickness, porosity, hydraulic conductivity and groundwater protective properties,

-WHAT? the layer-sharing properties of groundwater in the groundwater department,

-WHAT? a list of associated surface systems, including terrestrial ecosystems and surface waters, as the groundwater body is dynamically connected ;

-WHAT? estimates of the directions and the extent of the flow of water between the groundwater body and the associated surface systems ;

-WHAT? adequate data to calculate the long-term annual average rate of groundwater ; and

-WHAT? characterisation of the chemical composition of groundwater, including the specification of contributions from human activities. Typologias for groundwater characteristics may be used when the natural background levels for these groundwater bodies are determined.

3. Evaluation of the effects of human activities on groundwater

For groundwater bodies crossing the Danish-German border or, as a result of the characterization carried out in accordance with section 1, it may be deemed not to be able to meet environmental targets laid down for each occurrence of homecoming in section 7, paragraph 1, in the law of water planning, shall be collected and kept the following information, where appropriate, for each groundwater body :

-WHAT? the location of the sites of the groundwater body from which more than 3650 m is obtained annually ; 3 or from which water is obtained for at least 50 people,

-WHAT? the annual average abstraction from these sites,

-WHAT? the chemical composition of the water obtained by the groundwater body,

-WHAT? the location of the sites of the groundwater body to which water is directly derived,

-WHAT? the extent of the emissions in these places ;

-WHAT? the chemical composition of the wiring on the groundwater body, and

-WHAT? land use in the area (s) from which the groundwater body is added to water, including polluting loads and man-made changes to the infiltration of groundwater, e.g. discharges of the rainwater or the flow of the flow ; of the areas, artificial infiltration, containment or drainage.

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Appendix 2

Financial analysis of water use

The economic analysis shall, bearing in mind the cost of collecting the relevant data, contain sufficient information in sufficient detail to allow the following :

-WHAT? the relevant calculations necessary to ensure in accordance with the law of payment rules for waste water undertakings and the law of water supply to take account of the principle of cost recovery services for water, taking into account the need for water, taking into account : long-term forecasts of supply and demand for water in the river basin district, and, if necessary :

-WHAT? estimates of quantities, prices and costs of services relating to water, and

-WHAT? forecasts of relevant investments, including forecasts for such investments ;

-WHAT? estimates the combination of measures relating to water-use, which are the most cost-effective and can be included in the programme of measures laid down in section 19 (1). 1, in the case of water planning, with a view to estimates of the potential costs of such measures.

1) The announcement contains provisions which implement parts of Directive 2008 /105/EC of the European Parliament and of the Council of 16. In December 2008 on environmental quality standards in the water policy, amending and subsequently repealing Council Directive 82 / 1 7 6 / EEC, 83 /513/EEC, 84 /156/EEC, 84 /491/EEC and 86 /280/EEC and amending Directive 2000 /60/EC of the European Parliament and of the Council 2008, no. L 348, s. EUR 84 and parts of Directive 2000 /60/EC of the European Parliament and of the Council of 23. In October 2000, laying down a framework for the Community's water policy measures (the Water Framework Directive), the Official Journal of the European Union (Water Framework Directive). L 327, page 1.