5/2011 Sb.
DECREE
of 20 December. December 2010
on the definition of the main resorts of hydro-geological and groundwater, how
reviews the State of the groundwater and the constituent survey programmes and
evaluation of groundwater status
264/2015: Sb.
Ministry of environment and Ministry of agriculture lays down
pursuant to § 21 para. 3 of Act No. 254/2001 Coll. on waters and amending certain
acts (the Water Act), as amended by Act No. 20/2004 Coll. and Act No.
150/2010 Coll.:
TITLE I OF THE
INTRODUCTORY PROVISIONS
§ 1
The subject of the edit
This Decree incorporates the relevant provisions of the European Union ^ 1) and
covers:
and the way the definition of hydrogeological main resorts), the definition of bodies
waters,
(b)) the condition assessment method of groundwater and
(c)) the details of survey programmes for, and assessment of the State of groundwater.
§ 2
Definition of terms
For the purposes of this Ordinance, means the
a) pollutant substance that may endanger the quality of groundwater,
(b)) the input of pollutants into groundwater, the direct or indirect
the introduction of pollutants into groundwater as a result of human
activities,
c) groundwater quality standard, a standard of the environmental quality,
expressed as the concentration of a particular pollutant or group of pollutants
or the value of the indicator of pollution in groundwater, which should not be
exceeded in order to protect human health and the environment,
d) threshold of the environmental quality standard that is listed in the
table 1 of annex 5 of this order,
(e) the value of the reference value) concentration of a pollutant or
indicator of pollution in groundwater, which indicates
the impact of human activity and the deterioration of these waters,
(f) significant and sustained upward) trend any statistically and from
environmentally significant increase of concentration of a contaminant
the substances or groups of substances or the values of the indicator of pollution of groundwater
waters, for which it is necessary to reverse this trend and to establish the origin of tipping
This trend in accordance with section 9 and part (B) of annex 2 to this Decree,
(g) the concentration of the substance concentration) or pointer value,
that corresponds to the conditions, which are not affected by human activities,
(h)) to the default levels of average annual value of the results of the survey programmes
groundwater status at least from the years 2007 and 2008, or, in the case of substances
identified after the expiry of those years, during the first period,
for which it is available the representative period of monitoring data,
I) monitoring type and place of sampling point of groundwater, or
water immediately rising from springs or the place where it is located
stable equipment designed to monitor the status of the layers or levels
the groundwater or the richness of sources, and not covered by the
authorization to the treatment of waters,
j) monitoring the place of type B instead of sampling of groundwater, or
water immediately rising from springs or the place where it is located
stable equipment designed to monitor the status of the layers or levels
the groundwater or the richness of sources, and covered by the authorisation
to waste waters ^ 2)
the groundwater monitoring network) file monitoring sites by
the letters i and j)) that is provided for in the respective programme monitoring,
l) network detection of groundwater status file monitoring sites
According to the letter i) and (j)), the results of which will be used for the evaluation of the State of
groundwater and groundwater quality,
m) kontaminačním a cloud focused cloud of pollutants, which
can spread in the groundwater.
TITLE II
DEFINITION OF THE MAIN RESORTS AND THE DEFINITION OF HYDROGEOLOGICAL GROUNDWATER
§ 3
Definition of hydrogeological main resorts
(1) the hydrogeological rajony are defined on the basis of natural
characteristics, in particular in accordance with hydrogeological conditions of fissure type of aquifer and
circulation of groundwater.
(2) the hydrogeological rajony are composed of one or more services
groundwater.
(3) the list of hydrogeological main Resorts is listed in Appendix 6 of this
the Decree.
(4) details of borders and location of hydrogeological main resorts are
registered in accordance with section 22 paragraph 1. 4 (b). and) Water Act.
§ 4
The definition of groundwater
(1) the list of groundwater is given in Appendix 6 of this
the Decree.
(2) those groundwater bodies are defined in the depth of the top, base and
the deep layer.
(3) data on the location and boundaries of groundwater are recorded in
accordance with section 22 paragraph 1. 4 (b). and) Water Act.
TITLE III
§ 5
Evaluation of groundwater status
Evaluation of groundwater status consists of
and condition assessment) of groundwater,
(b)) the evaluation of significant and sustained upward trends and kontaminačních
clouds and
c) evaluation of the quality of groundwater.
§ 6
How to evaluate the status of bodies of groundwater
(1) the assessment of the status of bodies of groundwater lies in the evaluation of their
the chemical and quantitative status.
(2) to evaluate the status of bodies of groundwater are used results
obtained from the network discovery State groundwater analyses of General and
water catchment area of the characteristics and evaluation of the impact of human
the activities of the status of bodies of groundwater.
(3) the assessment of the status of bodies of groundwater cross-border
takes place in cooperation of the parties concerned within the framework of the International Commission ^ 3).
(4) in the graphical representation of the good status of groundwater
indicates a green and non-compliance with the color red.
§ 7
The method of assessment of the chemical status of bodies of groundwater
(1) the assessment of the chemical status of bodies of groundwater shall be carried out for the
all groundwater bodies once every six years, the procedure
as defined in annex 3 to this notice.
(2) the assessment of the chemical status of bodies of groundwater, the risk
done at least for all pollutants such
the designation makes a contribution.
(3) the assessment of the chemical status of bodies of groundwater are used
groundwater quality standards. If the administrator or authorized Professional basin
body referred to in section 21 para. 4 water act with regard to the results of the
the detection and assessment of the State of groundwater for the body
water assumes that the groundwater quality standards could thwart
achievement of the environmental objectives of related departments
surface waters referred to in Section 23a of the water law or result in a significant
the deterioration of the ecological or chemical quality of such bodies, or to
significant damage to terrestrial ecosystems which are at the service of the
groundwater directly dependent, shall establish in accordance with table No 1 of the annex
# 5 of this Ordinance more stringent threshold values. Programmes and measures
related to these thresholds shall apply also for
the activities provided for in § 33 of the Water Act and the Government Ordinance on the determination of
vulnerable zones and action programme ^ 10).
(4) the results of the assessment of the chemical status of bodies of groundwater,
express the classification of a good or unsatisfactory.
§ 8
The method of assessment of the quantitative status of groundwater
(1) the assessment of the quantitative status of groundwater bodies shall be carried out
for all groundwater bodies once every six years, the procedure
as defined in annex 4 of this order.
(2) the results of the assessment of the quantitative status of groundwater is
express the classification of a good or unsatisfactory.
§ 9
Method of evaluation of significant and sustained upward trends and reviews
kontaminačních clouds
(1) the evaluation of significant and sustained upward trends shall be carried out for the
of a pollutant, group of pollutants or values
indicators of pollution found in bodies of groundwater risk
once every six years under the conditions defined parts and annex 2 to the
This Decree.
(2) the results of the evaluation of significant and sustained upward trend in the
expressed as identified or unidentified significant and sustained
the upward trend.
(3) For identified significant and sustained upward trends shall be
the beginning of a reversal of this trend in accordance with part B of annex 2 to this
the Decree as a percentage of the level of the groundwater quality standards
set out in table 1 of annex 1 to this notice and threshold
values.
(4) in the identification of significant and sustained upward trends
pollutants that occur naturally and the influence of human
activities, taking into account the default levels, and if there are any, to data
the data collected before the start of the monitoring of the relevant programmes.
(5) for the evaluation of significant and sustained upward trends are used
the data from the operational monitoring and surveillance, and monitoring shall be determined
year or period from which trend identification records.
(6) the basis for the evaluation of significant and sustained upward trends is
in particular, the evaluation of the quality of groundwater and the assessment of the evolution of the quality
groundwater.
(7) the assessment of kontaminačních clouds is performed once every six years for
all free from the clouds, which may endanger the objectives of water protection as
environmental, and consists in the evaluation of trends in pollutants
substances identified in them.
(8) the result of the evaluation of the trends of pollutants in kontaminačních
the clouds referred to in paragraph 7, the information about the direction of propagation kontaminačních
clouds, their impact on the chemical status of bodies of groundwater, and the risk
that may pose to human health and the environment.
(9) when the graphical representation is significant and sustained upward trend
of pollutants indicates a black dot, the beginning of a reversal of a significant
and sustained upward trend indicates the blue dot.
§ 10
Method of evaluation of the quality of groundwater
(1) the evaluation of the quality of groundwater is carried out once a year for the
individual monitoring points the procedure defined parts and annex No. 5
to this Decree.
(2) shall apply to the evaluation of the quality of the reference values set out in
Annex No. 5 to this Decree.
§ 11
Method of evaluation of development of groundwater quality
(1) the development of groundwater quality Evaluation shall be carried out once every three
years for each of the monitoring procedure defined space, part B
Annex No. 5 to this Decree.
(2) the result of the evaluation of the development of groundwater quality is rising,
the declining trend in the concentrations of the individual fixed or polluting
the substances or their indicators.
§ 12
Ensure the quality system
Survey on the situation of the groundwater shall be carried out by laboratories which:
and have established quality system) in accordance with the Act on technical
requirements for products ^ 4) and in accordance with ČSN EN ISO/IEC 17025,
b) interlaboratory comparison programs participate in tests
organized to accredited organizations (ISO/IEC Guide 43-1)
that cover the entire range of indicators in the context of checking system status
the waters of the laboratory pursues and
(c)), the national accreditation body shall demonstrate competence through the implementation of
analyses of available reference materials typical for samples,
that contain the appropriate values of the concentrations in relation to the competent
environmental quality standards.
section 13 of the
The minimum performance criteria of methods of analyses
(1) the minimum performance criteria for all the methods have
the level of the relevant quality standards and threshold values for groundwater
combined extended measurement uncertainty (U2k) 50% or lower. The limit of
of determination is equal to or below 30% of the corresponding quality standards
groundwater and threshold values.
(2) If, for a given indicator there is appropriate quality standard
groundwater or there is no method of analysis that meets the minimum
performance criteria referred to in paragraph 1, such indicators will monitor
implemented best available techniques not entailing excessive
costs. The rationale and the description of the best available techniques shall be indicated
in the respective programme monitoring.
§ 14
Processing of the results of the analyses of chemical indicators
(1) the scope of the analysis of the chemical parameters is given to each
monitoring programmes.
(2) in order to ensure an acceptable degree of accuracy and precision for the purposes
evaluation of water status with relevant quality standards for groundwater, taking into
account the combined expanded measurement uncertainty (U2k).
(3) if the value of the indicators in a given sample are below the limits
of determination, measurement results for calculating average values
shall be at half the value of the limit of determination.
(4) if the mean value of the measurement results, calculated according to the procedure
paragraph 3 is below the limit of determination, the value is
referred to as less than the limit of determination.
(5) paragraph 3 shall not apply in the case of groundwater quality standards for
total pesticides set out in annex 1 to this notice, or in the
cases where it is a pointer that is part of the overall sum
the Group of indicators including their daughters or reaction products
or metabolites. In this case, the result is below the limit of determination
and shall not be counted in the Grand total includes only the values
individual indicators in the group above the limit of determination.
§ 15
The groundwater monitoring network
(1) groundwater monitoring network is proposed in accordance with the framework
program assessment and evaluation of water status and protected areas of the Czech
Republic (hereinafter referred to as "the framework programme monitoring"), and according to the purpose,
divided into:
and) monitoring network of groundwater chemical status,
b) monitoring network of groundwater quantitative status.
(2) monitoring network of groundwater chemical status is proposed,
to provide a coherent overview of groundwater quality in the Sub-basin,
allow to identify significant and sustained upward trends
pollutants and to assess the chemical status of bodies of
groundwater pursuant to this Ordinance.
(3) monitoring network of groundwater quantitative status is proposed
so that:
and reliable data) provided to assess the quantitative status bodies
of groundwater, or groups of bodies of groundwater in accordance with this Ordinance,
including evaluation of usable quantities of groundwater, natural
sources, levels and modes, a spreading rate of groundwater,
(b)) contained a number of representative monitoring points and the frequency of
measurements in the range, enabling the progress of the groundwater level,
an estimate of the size and direction of flow of groundwater levels and mode
yield in each body of groundwater or group of bodies of groundwater
waters with regard to the short-term and long-term variability of their
refilling,
(c)) for bodies of groundwater at risk provide you with such density
monitoring points and the frequency of measurements that will allow the evaluation of the impact of
abstractions and discharges on the layer mode and a spreading rate of groundwater and
associated bodies of surface water, aquatic and terrestrial ecosystems,
(d)) for groundwater bodies that have a cross-border nature,
ensure the number of monitoring sites and the frequency of measurements that will allow
provide an estimate of the size and direction of the groundwater flow and the findings
influence mode levels and rate of groundwater.
TITLE IV
ESSENTIALS OF SURVEY PROGRAMMES FOR AND ASSESSMENT OF THE STATE OF GROUNDWATER
section 16 of the
Programs for the detection and assessment of the State of groundwater
(1) Programmes for the detection and assessment of the State of groundwater are:
and) the framework programme monitoring,
(b) groundwater monitoring Program),
c) exploratory Programs of monitoring.
(2) the monitoring of groundwater pursuant to paragraph 1. (b))
composed of:
surveillance monitoring Programme) groundwater
(b) operational monitoring Programme) groundwater
(c) the Monitoring Programme) groundwater quantitative status.
(3) a body to ensure the survey programmes and assessment of the State
groundwater in accordance with approved programs of monitoring assesses the
intervals not exceeding three years, the progress and performance of the individual
monitoring programmes.
(4) the programme of surveillance monitoring of groundwater, the Program operation
monitoring of groundwater quantitative status and Program monitoring
groundwater will be updated no later than six years from their
approval, and at the latest on 31 December 2001. October of the preceding
of the calendar year.
Groundwater monitoring program
§ 17
Surveillance of groundwater monitoring program
(1) surveillance of the monitoring Program is based on the framework programme
monitoring is the basis, in particular, for
and additions and verify the results) the analysis of General and water management
the characteristics of the river basin and evaluation of the effects of human activity on the status of the
groundwater,
(b) the assessment of the chemical status of all) of groundwater and
the identification of significant and sustained upward trends of pollutant
substances,
(c) the long-term development of quality) evaluation caused by changes in the natural
conditions,
d) evaluation of the quality of groundwater,
(e)), the water balance management
(f) appropriate and effective suggestions) to update other programs
monitoring,
g) planning in the areas of water,
h) international monitoring programs, and for the purposes of cooperation in the
international river basin areas,
I) draft programmes of measures pursuant to section 26 of the water law.
(2) the surveillance monitoring shall, in particular:
and) monitoring network of groundwater chemical status, including a list of
monitoring sites,
b) watch list indicators, frequency of monitoring for each
monitoring space, including requirements for reliability and accuracy
the results, while at all monitoring points are, without exception,
tracked indicators: oxygen, pH, conductivity, nitrates and
ammonium ions.
(3) at selected monitoring sites high-risk bodies
the waters are monitored by indicators that such designation of a body
groundwater contribute. The selected monitoring location in this
the meaning of means monitoring a place that may affect the impact of human
the activities identified in the framework of the evaluation of the effects and impacts on the status of the
groundwater.
(4) on the selected monitoring points of groundwater
the cross-border nature of those indicators are tracked, which
apply to protect all uses of a given body of groundwater
dependent on the flow of water. These indicators are set out in the framework of the
cooperation in international commissions ^ 3).
(5) the programme of surveillance of monitoring is proposed on the basis of the analyses
General and water management River basin characteristics and evaluation
the impact of human activity on the status of the groundwater for each period
the validity of the river basin management plans.
section 18
Operational monitoring of the groundwater program
(1) the operational monitoring of the groundwater Program is based on the Framework
program monitoring is the basis, in particular, for:
and the assessment of the chemical status of the risk) of groundwater and
the identification of significant and sustained upward trends of pollutant
substances,
b) evaluation of the quality of groundwater,
(c) the management of the water balance,)
(d) in the area of water planning),
(e)) the international monitoring programs, and for the purposes of cooperation in the
international river basins and areas
f) proposals for programmes of measures pursuant to section 26 of the water law.
(2) the operational monitoring shall, in particular:
and) monitoring network of groundwater chemical status, including a list of
monitoring sites,
(b)) the lists of controlled indicators and frequency of monitoring for each
monitoring space, including requirements for reliability and accuracy
results, whereby:
1. the monitoring points of the relevant risk of a body
the waters are monitored by indicators of pollutants, that such
designation of groundwater,
2. the monitoring points, where the results of the evaluation of the quality suggest
75% reached the level of the quality standards laid down in annex No. 1.
This order and the thresholds, the indicators are tracked
pollutants, for which this was achieved.
(3) the operational monitoring Programme is carried out in the years when it is not
carried out surveillance monitoring Programme.
§ 19
The program of monitoring of groundwater quantitative status
(1) a Program of monitoring of groundwater quantitative status is based on the
The monitoring of the framework programme and is the basis for:
and) reviews of groundwater quantitative status,
(b) the levels and mode) the evaluation of the strength of the sources of groundwater, including
their long-term trends and the balance between replenishing and subscriptions
groundwater,
(c)) the evaluation of the natural resources of groundwater,
(d) water balance) management pursuant to § 22 of the Water Act,
e) planning in the areas of water,
f) proposals for programmes of measures pursuant to section 26 of the water law.
(2) the monitoring of groundwater quantitative status provides
in particular:
and) monitoring network of groundwater quantitative status, including
the list of monitoring sites and their number,
(b) monitoring of and) the frequency of the strength of the sources for each monitoring
instead.
section 20
Reconnaissance monitoring programs
(1) Programmes of investigative monitoring shall be based on the framework programme
monitoring and provides:
and the reasons for the introduction of the survey) the monitoring, the objectives of the survey
monitoring and its links to other programs, monitoring,
(b)) the definition of monitoring sites,
(c)) the lists of controlled indicators and frequency of monitoring for each
the monitoring location.
(2) the programmes of investigative monitoring shall be applied:
and) where there were extraordinary phenomena and their causes are not known,
(b)) in the event that the results of surveillance monitoring and evaluation trends
indicate the probability of failing to achieve good water status and the water
the Department has not yet been included in the programme, operational monitoring,
(c)) in order to determine the size and impact of accidental pollution, or
(d)) in order to provide information for the establishment of a programme of measures to
achieving the objectives of water protection.
(3) the exploratory Programs of monitoring are processed according to the needs,
always in relation to groundwater bodies.
(4) the initiative to deploy reconnaissance monitoring gives an administrator the catchment area according to the
section 54 of the Water Act, the Czech environmental inspection, the municipality with
expanded authority or designated expert body pursuant to § 21 para. 4
Water Act.
section 21
The effectiveness of the
This Decree shall take effect on the 15th day following the date of its publication.
The Minister of the environment:
Mgr. Drobil in r.
Minister of agriculture:
Ing. Fuksa in r.
Annex 1
The quality standards and the way the establishment of threshold values
Part A: groundwater quality standards
Table 1: groundwater quality standards
+---------------------------------------+---------------------------------------+
| Polluting substance | Quality standard |
+---------------------------------------+---------------------------------------+
| Nitrates | 50 mg/l |
+---------------------------------------+---------------------------------------+
| The active substances in pesticides | 0.1 µ g/l |
| including their major | 0.5 µ g/l (total pesticides) * |
| metabolites, degradation, and ||
| reaction products * | |
+---------------------------------------+---------------------------------------+
Explanatory notes:
Pesticides means preparations according to § 2 (2). 2 (a). g) of law No.
326/2004 Coll., on phytosanitary care and amendments to certain acts, and
biocidal products under section 2 of the Act No. 120/2002 on the conditions for the marketing of
biocidal products and active substances on the market and amending certain
related laws.
** "Pesticides" means the sum of all individual pesticides that
have been identified and which have been established under section 7 to 15 of this
the Decree.
Part B: method of determining threshold values groundwater
(1) the threshold values shall be established for all the pollutants and
indicators of pollution, on the basis of those groundwater bodies
referred to as being at risk.
(2) the Threshold values for the pollutants or indicators of pollution,
down so that when their excess at the monitoring site was not
one or more of the conditions of good chemical status in accordance with annex
# 3 of this order.
(3) the thresholds shall be determined having special regard to their impact on the
associated bodies of surface water, aquatic ecosystems, and the related
terrestrial ecosystems; are taken into consideration, inter alia, toxicology and
ecotoxicological properties.
(4) when the establishment of threshold values shall take account of:
and) range of interactions between groundwater and related
bodies of surface water, aquatic ecosystems, and the related
terrestrial ecosystems,
(b)) violation to actual or potential legitimate uses or
features of groundwater,
c) all pollutants, on the basis of the services of the underground
water indicate at risk, taking into account the minimum list
as set out in table 2 of this annex,
(d) the hydrogeological characteristics), including information on natural
concentrations and the water balance,
(e)) the origin of pollutants, their possible natural occurrence, their
toxicity and tendency to move around in the soil and aquifers,
their persistence and their bioaccumulation potential,
(f) data quality and scope) of the available data on the basis of the threshold
the values set, access different analytical methods in the determination of
the natural concentration of substances which may occur both naturally,
and, as a result of human activity.
(5) if there is a natural increase in the concentrations of substances or ions
or their indicators, on the basis of natural hydro-geological causes
you need to take into account these natural concentration for a given Department
groundwater in establishing the threshold values.
(6) the thresholds shall be at the level of a body of groundwater; threshold
values may be the same for multiple bodies of groundwater; When determining the
threshold values for groundwater bodies that have international
character or for bodies of groundwater that are found in the
international river basin district lays down threshold values in cooperation with
international commissions ^ 4).
(7) the list of threshold values will change if new information about
groups of pollutants, or indicators of pollution substances
suggest that the threshold should be established for other substance
or modified an existing threshold or threshold again
the value that was previously deleted from the list.
(8) the threshold values can be removed from the list if it is not already the
competent groundwater pollutants, groups of
of pollutants, or indicators of pollution risk.
Table 2: minimum list of pollutants and their indicators
+---------------------------+---------------------------+---------------------------+
| Substances, ions | Artificially produced | The parameters showing |
| may be present | synthetic fabrics | on the latter, or |
| naturally or as a result of | | other intrusions |
| human activity | | |
+---------------------------+---------------------------+---------------------------+
| Arsenic | Trichloroethylene | Conductivity |
| Cadmium | Tetrachloroethylene | |
| Lead | | |
| Mercury | | |
| Ammonium | | |
| Chloride | | |
| Sulphate | | |
+---------------------------+---------------------------+---------------------------+
Annex 2
Significant and sustained upward trend and the beginning of a reversal of the trend
Part a: conditions for the identification of significant and sustained upward trends
For the purposes of the identification of significant and sustained upward trends are:
and monitoring the program constructs), so that the frequency of monitoring and
the location of the monitoring sites:
i. provides the information necessary to ensure that such upward trends
It will be possible with sufficient accuracy and reliability to distinguish it from
natural fluctuations,
II. the identification of these early enough allows upward trends,
in order to carry out measures to prevent environmentally significant
deterioration in the quality of groundwater or is at least as much as possible
to mitigate this,
III. taking into account the current physical and chemical characteristics of the Department
groundwater, including groundwater flow conditions, speed
their recovery and the time of infiltration soil or subsoil,
(b)) the methods for monitoring and analysis, which are in accordance with § 17 and
section 18 of the Ordinance, where appropriate with the methods (methods issued by the
European Committee for Standardization) or national standardised methods, to
methods, so as to ensure the same professional quality and comparability of
the collected data,
(c)) for the analysis of trends at individual monitoring points shall apply
statistical methods such as regression analysis,
d) all measurements below the limit of determination, with the exception of
indicators, where their sum (e.g. pesticides) laid down in the
table 1 of annex 1 of this order, assigns half the value
the upper limit of determination demonstrated in time series.
Part B: how to identify the beginning of a reversal of significant and sustained
upward trend
(1) in the beginning of the reversal of a trend shall be regarded as the achievement of concentration
pollutants at a level of 75% of the value of groundwater quality standards
listed in table 1 of annex 1 of this order, and thresholds
If:
I need not be fixed before the trend reversal so that measures
leading to a trend reversal as efficiently as possible avoid environmentally
significant deterioration of the quality of groundwater, or at least the most
mitigate, or
II. There is no reason the determination of the beginning of trend reversals before, because it is
due to the limit of the impossible figure trend corresponding to level 75
% of the groundwater quality standards listed in table 1 of the annex
No. 1 of this Decree and the thresholds.
(2) the trend reversal can be determined at a later stage, if the speed
increasing options and trends are such that a later starting
measures to change the trend still allows the efficient prevention of any
environmentally significant detrimental changes in groundwater quality or its
mitigate as far as possible. Such a determination shall not lead to any
delay, as regards compliance with the deadlines of the objectives of water protection ^ 5).
(3) for the activities provided for in other legislation ^ 6) ^ 7), the initial
point for implementing measures to reverse the trend established in accordance with
the requirements of that legislation and the requirements of the objectives of protection
waters. ^ 5)
(4) as soon as the risk of groundwater determined the origin of the
reversal of the trend according to the previous provisions, it cannot be during the six-year
River basin management plan change.
Annex 3
Procedure for the assessment of the chemical status of bodies of groundwater
Part a: the criteria of good groundwater chemical status and unwanted
waters
(1) the chemical status of a body of groundwater, it is considered good if:
and the results of the monitoring) of groundwater:
1. do not show any signs of zasolení or other vniků pollutants
substances into groundwater,
2. polluting substances are not such as to have caused the failure
the objectives of the protection of water related bodies of surface water, the deterioration of the
chemical or organic status of these bodies of surface water, or
damage directly dependent terrestrial ecosystems,
(b)) the values of the groundwater quality standards or threshold values
set out in table 1 of annex 5 of this Decree are not exceeded
at any monitoring point in that body of groundwater or group of
bodies of groundwater.
(2) if the value of the quality standards or threshold laid down in
table 1 of annex 5 of this order is exceeded on one or more
monitoring points, the groundwater body done
the investigation procedure laid down in part B of this annex.
(3) the chemical status of a body of groundwater, it is considered good if
the investigation carried out in accordance with paragraph 2 shows that
and the concentration of pollutants in excess of) quality standards
groundwater or thresholds set out in table 1 of the annex.
5 of this Ordinance pose a significant risk to the environment, and
taking into account the extent of the groundwater,
(b)) are subject to the conditions laid down in point a) of paragraph 1 of this annex,
(c)) have met the requirements for protected areas established pursuant to
special legislation ^ 8) and
d) function of groundwater from which groundwater is used
for the various needs of society, in particular for the supply of the population
drinking water has not been significantly impaired by pollution.
(4) the chemical status of a body of groundwater, it is considered unsatisfactory,
If you are not satisfied the conditions of good chemical status of a body
groundwater as defined in paragraphs 1 to 3 of part A of this annex.
Part b: Particulars of the investigation
(1) the investigation carried out in the cases referred to in paragraph 1. 2 part A of this
the annex to take account of:
and) information collected in the context of the analysis of General and water management
the characteristics of the river basin, reviews the impact of human activity on the status of the services
groundwater ^ 3),
(b)) the results from the monitoring network obtained in accordance with sections 7 to 12 of this
the Decree,
c) any other relevant information, including a comparison of arithmetic
average annual concentrations of the relevant pollutants at one
monitoring point with the groundwater quality standards values
set out in table 1 of annex 1 of this order and the threshold
values.
(2) in the cases referred to in point (a)), and (d)). 3 of part A of this annex
additional examination is carried out, which preliminarily estimates the extent to which
exceed the annual arithmetic mean concentration of a pollutant standard
groundwater quality or threshold. This investigation shall be carried out on
the basis of the relevant summary of the survey results, or with the help of
concentration estimates based on the conceptual model of a body or a group of
bodies of groundwater.
(3) in the cases referred to in point (b)), and (c)). 3 of part A of this annex
additional examination is performed to evaluate:
and the impact of pollutants on) of groundwater,
(b)) the quantities and concentration of pollutants that are
transported, or there is a likelihood that they could be
transported from the body of groundwater to the associated surface waters
or directly dependent terrestrial ecosystems,
(c)) the likely impact of the quantity and concentrations of the pollutants
transported by the associated surface waters and directly dependent
terrestrial ecosystems,
d) extent and other vniků to groundwater,
e) threat which pollutants in groundwater
represent for the quality of water intended for human consumption.
Annex 4
Procedure for the assessment of groundwater quantitative status
(1) the quantitative status, it is considered good if:
and) the level of the groundwater levels in the groundwater body is such that
the amount of usable resources ^ 9) ground water products is a long-term
average annual quantity of listings and at the same time,
(b)) the level of ground water is not exposed to changes caused by
human activities that would:
1. the failure to achieve the objectives of water protection for the associated bodies of surface water,
2. any significant deterioration in the status of these waters,
3. any significant damage to associated terrestrial ecosystems.
c) changes in the directions of groundwater flow in groundwater
resulting from changes in levels occur temporarily, or consistently in
a spatially limited area, but do not indicate a penetration of pollutant
substances, or falling and clearly identifiable impact of human activity in the
the direction of flow, which could cause such intrusion.
(2) the Quantitative status of a body of groundwater, it is considered
unsatisfactory, if the conditions are not fulfilled, good quantitative
status of a body of groundwater as defined in paragraph 1 of this annex.
Annex 5
The procedure for evaluation of the quality and development of groundwater quality
Part a: procedure for evaluation of groundwater quality
(1) for the evaluation of groundwater quality will make use of the results obtained from
surveillance programs or operational monitoring (hereinafter referred to as the ' competent
program monitoring "), and data obtained through requirements
other legislation ^ 2).
(2) the evaluation of the quality of groundwater is done for all
monitoring sites monitoring network of groundwater chemical status
the program monitoring.
(3) the evaluation of the quality of groundwater is done for the indicators set out
in the respective programme monitoring, at least for all parameters
set out in table 1 of this annex.
(4) the evaluation of groundwater quality monitoring points for that
are not part of the monitoring network of groundwater chemical status,
done for all parameters that are obtained through the
the requirements of other legislation ^ 2), and at the same time are set out
the relevant monitoring programs.
(5) the evaluation of the quality of groundwater lies in a comparison of average annual
(arithmetic mean) of the values of the individual monitoring points with
the appropriate quality standard or the threshold. In cases where it is
There is only one measurement, the average value does not apply.
(6) the result of the evaluation of the quality of groundwater for substances and indicators
Group A (table 1 of this annex) is compliant or noncompliant
the quality of groundwater.
(7) groundwater quality is considered satisfactory, if no
the average annual value does not exceed the indicators to the monitoring site
quality standard or the threshold value given in table no. 1 of this
of the annex.
(8) the result of the evaluation of the quality of groundwater for the characteristics of the Group (B)
(table 2 of this annex) is the presence or absence of the potential impact of human
activity.
(9) the result of the evaluation of the quality of groundwater for the characteristics of the Group (C)
(table 3 of this annex) is only a determination of their average annual
values.
Table 1: list of pollutants and indicators and their values for the Group and
----------------------------------------------------------------------------------------------------
Substance name CAS Unit Standard threshold
the quality of the
----------------------------------------------------------------------------------------------------
acetochlor 34256-82-1 0.1 µ g/l
acetochlor ESA 187022-11-3 0.1 µ g/l
acetochlor OA 194992-44-4 0.1 µ g/l
alachlor 15972-60-8 0.1 µ g/l
alachlor ESA 142363-53-9 0.1 µ g/l
alachlor OA 171262-17-2 0.1 µ g/l
ammonium mg/l0, 21-0.51
anthracene 120-12-7 µ g/l0, 1
arsenic and its compounds 7440-38-2 µ g/l10
Atrazine 1912-24-9 µ g/l0, 1
bentazone 25057-89-0 0.1 µ g/l
benzene 71-43-2 µ g/l1
benzo (b) fluoranthene 205-99-2 µ g/l0, 03
benzo (k) fluoranthene 207-08-9 µ g/l0, 03
benzo (g, h, i) perylen 191-24-2 µ g/l0, 002
benzo (a) pyrene 50-32-8 µ g/l0, 01
clopyralid 1702-17-6 0.1 µ g/l
p, p-DDT 50-29-3 µ g/l 0, 10, 01
desethylatrazin 6190-65-4 0.1 µ g/l
dicamba 1918-00-9 0.1 µ g/l
2.4-dichlorophenoxy acetic 94-75-7 0.1 µ g/l
acid (2.4-D)
dimetachlor 50563-36-5 0.1 µ g/l
nitrate mg/l 5015.05-19.92
nitrites mg/l0, 5
fluoranthene 206-44-0 µ g/l0, 1
phosphates mg/l0, 5
hexazinon 51235-04-2 0.1 µ g/l
aluminum and its compounds 7429-90-5 µ g/l200
indeno (1, 2, 3-cd) pyrene 193-39-5 µ g/l0, 002
chloridazon 1698-60-8 0.1 µ g/l
chlorides mg/l200
chlorotoluron 15545-48-9 0.1 µ g/l
Chlorpyrifos 2921-88-2 µ g/l 0, 10, 03
isoproturon 34123-59-6 0.1 µ g/l
cadmium and its compounds 7440-43-9 µ g/l0, 25
cyanide total 5-12-5 µ g/l500
acid-neutralizing capacity, mmol/l0, 2
to pH 4.5
metolachlor 51218-45-2 0.1 µ g/l
metolachlor ESA 171118-09-5 0.1 µ g/l
metolachlor OA 152019-73-3 0.1 µ g/l
naphthalene 91-20-3 µ g/l0, 1
nickel and its compounds 7440-02-0 µ g/l20
lead and its compounds 7439-92-1 µ g/l5
pesticides (sum) 0.5 µ g/l
prometryn 7287-19-6 0.1 µ g/l
Mercury and its compounds 7439-97-6 µ g/l0, 2
simazine 122-34-9 0.1 µ g/l
sulphates mg/l400
terbuthylazin 5915-41-3 0.1 µ g/l
terbuthylazin desethyl 30125-63-4 0.1 µ g/l
terbuthylazine hydroxy 66753-07-9 0.1 µ g/l
terbutryn 866-50-0 0.1 µ g/l
tetrachlorethen (PER)
1, 1, 2-trichlorethen 127-18-4 µ g/l10 (sum)
79-01-6
trifluralin 1582-09-8 µ g/l 0, 10, 03
trichloromethane 67-66-3 µ g/l2, 5
CAS-a unique numeric identifier for chemical substances, polymers, biological sequences,
mixtures and alloys
____________________________
1 the threshold 0.21 and 0.3 applies to ground water with directly dependent surface water,
for other ground water apply threshold 0.5 mg/l.
1 for all groundwater, more stringent threshold applies only
2 more stringent threshold (15.05; 16.82 and 19.92 mg/l) apply to a underground vodys directly dependent
surface water, ground water for the others apply the threshold of 50 mg/l
3 for all groundwater, more stringent threshold applies only
threshold is the minimum
5 for all groundwater, more stringent threshold applies only
Table 2: list of pollutants or indicators and their values in Group B
--------------------------------------------------------------------------------
Substance name CAS Unit Reference
the value of the
--------------------------------------------------------------------------------
Naturally occurring substances
--------------------------------------------------------------------------------
antimony 7440-36-0 µ g/l 5
barium 7440-39-3 50 µ g/l
beryllium 7440-41-7 µ g/l 2
BOR 7440-42-8 µ g/l
16984-48-8 mg/l fluoride 1.5
chrome 7440-47-3 50 µ g/l
Cobalt 7440-48-4 3 µ g/l
Lithium 7439-93-2 µ g/l MS **
manganese 0.05 mg/l 7439-96-5
molybdenum 7439-98-7 µ g/l 5
Selenium 7782-49-2 µ g/l 10
sodium 7440-23-5 mg/l 200
Vanadium 7440-62-2 µ g/l 18
Zinc 7440-66-6 150 µ g/l
--------------------------------------------------------------------------------
Synthetic substances
--------------------------------------------------------------------------------
desethyl atrazine-desisopropyl 3397-62-4 0.1 µ g/l
(diaminoatrazin)
Atrazine-desisopropyl 1007-28-9 0.1 µ g/l
Atrazine-hydroxy 2163-68-0 0.1 µ g/l
azoxystrobin 131860-33-8 0.1 µ g/l
benzo (a) anthracene 56-55-3 0.1 µ g/l
bromacil 314-40-9 0.1 µ g/l
bromoxynil 1689-84-5 0.1 µ g/l
carbendazim 10605-21-7 0.1 µ g/l
carbofuran 1563-66-2 0.1 µ g/l
cyanazine 21725-46-2 0.1 µ g/l
o, p '-DDD 53-19-0 0.1 µ g/l
p, p '-DDD 72-54-8 0.1 µ g/l
o, p '-DDE 3424-82-6 0.1 µ g/l
p, p '-DDE 72-55-9 0.1 µ g/l
o, p '-DDT 789-02-6 0.1 µ g/l
desmetryn 1014-69-3 0.1 µ g/l
di (2-ethylhexyl) phthalate DEHP 117-81-7 1.3 µ g/l
dibenzo (a, h) anthracene 53-70-3 µ g/l 0.016
dichlobenil 1194-65-6 0.1 µ g/l
1.2-dichlorobenzene 95-50-1 0.1 µ g/l
1.3-dichlorobenzene 541-73-1 0.1 µ g/l
1.4-dichlorobenzene 106-46-7 0.1 µ g/l
1.2-dichloroethane 107-06-2 µ g/l 3
1.1-dichlorethen 75-35-4 0.1 µ g/l
1.2-cis-dichlorethen 156-59-2 0.1 µ g/l
1.2-trans-dichlorethen 156-60-5 µ g/l MS **
dichloromethane 75-09-2 0.1 µ g/l
dichlorprop-P 15165-67-0 0.1 µ g/l
dimethomorph 110488-70-5 0.1 µ g/l
dcmu 330-54-1 0.1 µ g/l
EDTA 60-00-4 µ g/l 5
ethofumesate 26225-79-6 0.1 µ g/l
Ethylbenzene 100-41-4 0.2 µ g/l
fenantren 85-01-8 µ g/l 0.005
fenhexamid 126833-17-8 0.1 µ g/l
fluazifop-p-butyl 79241-46-6 0.1 µ g/l
Fluorene 86-73-7 0.1 µ g/l
Alpha-hexachlorocyclohexane 319-84-6 0.1 µ g/l
Beta-hexachlorocyclohexane 319-85-7 0.1 µ g/l
gamma-hexachlorocyclohexane 58-89-9 0.1 µ g/l
chlorobenzene 108-90-7 0.1 µ g/l
chlorethen 75-01-4 µ g/l 0.5
chlorsulfuron 64902-72-3 0.1 µ g/l
chrysen 218-01-9 0.005 µ g/l
iprodione 36734-19-7 0.1 µ g/l
kresoxim-methyl 143390-89-0 0.1 µ g/l
lenacil 2164-08-1 0.1 µ g/l
linuron 330-55-2 0.1 µ g/l
MCPA 94-74-6 0.1 µ g/l
MCPB 94-81-5 0.1 µ g/l
mecoprop-P 16484-77-8 0.1 µ g/l
metalaxyl 57837-19-1 0.1 µ g/l
metazachlor 67129-08-2 0.1 µ g/l
methoxyfenozide 161050-58-4 0.1 µ g/l
metoxuron 19937-59-8 0.1 µ g/l
metribuzin 21087-64-9 0.1 µ g/l
metribuzin-desamino 35045-02-4 0.1 µ g/l
metribuzin desamino-diketo 52236-30-3 0.1 µ g/l
metribuzin-diketo 56507-37-0 0.1 µ g/l
monolinuron 1746-81-2 0.1 µ g/l
napropamide 15299-99-7 0.1 µ g/l
nicosulfuron 111991-09-4 0.1 µ g/l
NTA 139-13-9 µ g/l 5
PCB28 7012-37-5 µ g/l 0.007
PCB52 35693-99-3 µ g/l 0.007
PCB101 37680-73-2 µ g/l 0.007
PCB118 31508-00-6 µ g/l 0.007
PCB138 35065-28-2 µ g/l 0.007
PCB153 35065-27-1 µ g/l 0.007
PCB180 35065-29-3 µ g/l 0.007
1939-36-2 PDTA µ g/l MS **
pentachlorobenzene 608-93-5 0.1 µ g/l
picloram 1918-02-1 0.1 µ g/l
propachlor 1918-16-7 0.1 µ g/l
propiconazole 60207-90-1 0.1 µ g/l
pyrene 129-00-0 0.1 µ g/l
styrene 100-42-5 µ g/l MS **
sulfosulfuron 141776-32-1 0.1 µ g/l
tebuconazole 107534-96-3 0.1 µ g/l
carbon tetrachloride 56-23-5 0.1 µ g/l
thiophanate-methyl 23564-05-8 0.1 µ g/l
toluene 108-88-3 0.2 µ g/l
triadimefon 43121-43-3 0.1 µ g/l
triadimenol 55219-65-3 0.1 µ g/l
those ADIs being exceeded 82097-50-5 0.1 µ g/l
tribenuron-methyl 101200-48-0 0.1 µ g/l
1, 1-trichloroethane 79-00-5 2 µ g/l MS **
(2, 4, 5-trichlorfenoxy) acetic 93-76-5 0.1 µ g/l
acid (2, 4, 5-T)
triticonazole 131983-72-7 0.1 µ g/l
o-xylene 95-47-6 0.2 µ g/l
m + p-xylene µ g/l MS **
--------------------------------------------------------------------------------
General chemical and physical indicators
--------------------------------------------------------------------------------
absorbance (254 nm, 1 cm) the number of MS **
color mg Pt/l-
the total volume of Alpha activity Bq/l 0.3
humic substances 1415-93-6 mg/l MS **
COD-Mn mg/l 3
conductivity mS/m in the terrain, MS **
water temperature ° c 29
dissolved organic carbon 7440-44-0 mg/l 5
--------------------------------------------------------------------------------
The indicator is expressed as the sum of
--------------------------------------------------------------------------------
phenols myth with water vapour 0.5 mg/l
chloralkanes C10-13 85535-84-8 0.4 µ g/l
nonylfenoly 25154-52-3 µ g/l 20
oktylfenoly 1806-26-4 µ g/l MS **
PAU 0.15 µ g/l
PCB µ g/l 0.01
the sum of dichlorbenzenů with-DCB µ g/l 0.25
anionic tensides mg/l 0.3
hydrocarbons C10-C40 mg/l 0.1
--------------------------------------------------------------------------------
CAS-a unique numeric identifier for chemical substances, polymers, biological sequences,
mixtures and alloys
** MS-limit of determination
Table 3: list of pollutants and their indicators group C
---------------------------------------------------------------
Name of the indicator, CAS
---------------------------------------------------------------
potassium 7440-09-7 mg/l
magnesium 7439-95-4 mg/l
15593-90-5 mg/l silicates
copper 7440-50-8 µ g/l
strontium 7440-24-6 µ g/l
calcium 7440-70-2 mg/l
Iron mg/l 7439-89-6
---------------------------------------------------------------
Part b: Procedure reviews the evolution of groundwater quality
(1) for the evaluation of development of groundwater quality will make use of the results
obtained from the monitoring program and on the data obtained
through the requirements of other legislation.
(2) the assessment of the quality of groundwater development is done for all
monitoring sites monitoring network of groundwater chemical status
the program monitoring and for monitoring points for
that the data are acquired through other legal requirements
regulations.
(3) the assessment of the quality of groundwater development is done for indicators
laid down in the monitoring program, at least for all
indicators set out in table 1 of this annex.
(4) the assessment of the quality of groundwater development for monitoring sites,
that are not part of the monitoring network of groundwater chemical status
is performed for all parameters that are obtained through the
the requirements of other legislation, and at the same time are set out
the relevant monitoring programs.
(5) the assessment of the development of quality lies in the time analysis of measured values
during the period, at least from 2006 and 2007; for a sufficient length of the
the corresponding period is considered to be 10 years.
(6) the assessment of the evolution of the quality of the statistical method is used, for example,
linear regression.
Annex 6
A list of the main resorts of hydro-geological and groundwater
------------------------------------------------------------------------------------------------------------------------
The number of the name of the body of groundwater, the competent Department, Position name of the competent
groundwater hydrological hydrological circle
underground rajon
waters
------------------------------------------------------------------------------------------------------------------------
11100 Kvartér Eagle Kvartér Eagle upper 1110
11210 Kvartér Elbe after Hradec Kralove late 1121 Kvartér Elbe after Hradec Kralove
11220 Kvartér Labe in Pardubice, Kvartér after the late 1122 Elbe after Pardubice
11300 Kvartér Loucna and Chrudimka late 1130 Kvartér Loucna and Chrudimka
11400 Kvartér Elbe after top Kvartér 1140 Elbe Tynec upon Týnec
11510 Kvartér Elbe after Cologne top 1151 Kvartér Elbe after Cologne
11520 Kvartér Elbe after top Kvartér 1152 Elbe Nymburk after Nymburk
11600 Kvartér Urbanické Gates Urbanické Gates Kvartér upper 1160
11710 Kvartér Elbe after the Jizera river Elbe after the Cretaceous Kvartér 1171 Jizera
11720 Kvartér Elbe after the Vltava River Upper Elbe Kvartér 1172 after the Vltava River
11800 Kvartér Elbe after 1180 Upper Elbe Kvartér Pretoria after Lovosice
11900 Kvartér and neogén odravské Kvartér and the upper section of the 1190 neogén odravské parts
The Cheb basin of the Cheb basin
12110 Kvartér top Kvartér 1211 the Lužnice River Lužnice
12120 1212 Kvartér Kvartér Eva top Offers
12300 Kvartér Otava and Blanice late 1230 Blanic Otava and Kvartér
1310 13100 Kvartér Kvartér Czech Republic Czech Republic top
13200 Radbuza 1320 Kvartér Kvartér top Radbuza
13300 Kvartér May top Kvartér May 1330
14100 Kvartér Liberec basin late 1410 Kvartér Liberec basin
14200 Kvartér and Miocene Zittau basin and upper Kvartér Miocene 1420 the Zittau basin
the Frýdlant promontory 14300 Kvartér top Kvartér of the Frýdlant promontory 1430
15100 Kvartér Oder Kvartér Oder upper 1510
15200 Kvartér top Kvartér 1520 Opava Opava
15500 Kvartér Opava Opava upper 1550 Kvartér pahorkatina hills
16100 Kvartér top Kvartér Top Moravia 1610 the upper Morava
16210 Pliopeistocén Hornomoravský late 1621 Pliopeistocén Hornomoravský
Vale-Vale-northern part of the northern part of the
16220 Pliopeistocén Hornomoravský late 1622 Pliopeistocén Hornomoravský
the southern part of the Vale-Vale-South part
16230 Pliopleistocén Moor top Pliopleistocén Moor 1623
16240 Kvartér Valové, Romže, and Hana Valové, upper Kvartér 1624 Romže and Haná region
16310 Kvartér Horni Becva late 1631 Kvartér Horni Becva
16320 Kvartér Bottom Kvartér Lower upper Becva 1632 Bečva
16410 Kvartér Thaya late 1641 Kvartér Thaya
16420 Kvartér Jevišovky top Kvartér Jevišovky 1642
16430 Kvartér Svratka Svratka upper 1643 Kvartér
16440 Kvartér Jihlava late 1644 Kvartér Jihlava
16510 Kvartér Czech Republic top 1651 Kvartér Czech Republic
16520 Kvartér soutoké Moravia late 1652 Kvartér soutoké area of Moravia
and the Dyje and Dyje
21100 the Cheb basin base 2110 the Cheb basin (the Cheb basin)
21200 Sokolovská pan base 2120 Sokolovská Pan
21310 Mostecká pan-northern part of the base 2131 Mostecká pan-northern part
21320 Mostecká Pan-southern part of basic 2132 Bridge Pan-southern part
21400 Třeboň basin-southern part of basic 2140 Třeboň basin-southern part
21510 Třeboň basin-northern part of the base 2151 Třeboň basin-northern part
21520 Třeboň basin-the central part of the base 2152 Třeboň basin-middle part
21600 Budějovická pan base 2160 Budějovická Pan
2211 22110 Bečevská gateway Bečevská gateway base
22120 basic 2212 Oderská gateway Oderská gateway
22201 Hornomoravský úvaly-north part of the underlying bed of Hornomoravský 2220
22202 Hornomoravský bed-South part of the underlying bed of Hornomoravský 2220
22203 Hornomoravský úvaly-middle part of the underlying bed of Hornomoravský 2220
2230 22300 Val Val gateway core gateway
22410 Dyje-svratka's bed base 2241 Dyje-svratka's bed
22420 Kuřimská basin base 2242 Kuřimská basin
22501 Dolnomoravský úvaly-northern part of basic 2250 Dolnomoravský úvaly
22502 Dolnomoravský úvaly-middle part of the bed base Dolnomoravský 2250
22503 Dolnomoravský bed-South part of the base 2250 Dolnomoravský úvaly
Ostrava-ostravská basin 22610 part basic 2261 Ostrava-ostravská basin section
22620 Ostravská basin-karvinská part of the Ostrava basin-2262 base karvinská part
31100 Pavlov hills and around the base and around the hills of Pavlov 3110
32110 Flyš Alder basin Flyš basin base 3211 Alder
32121 Ostravice basin base Flyš 3212 Flyš in the catchment area of the Ostravice River
32122 Flyš in the catchment area of the river Ostravice-3212 Flyš after the base of the basin of the Ostravice River
Lučina River flows into the flow
32130 Flyš in mezipovodí Oder Flyš in mezipovodí base 3213 Oder
32210 Flyš in Bečva River basin base 3221 Flyš Becva
32221 Flyš in the basin of the Morava-northern part of the base of the basin of the Morava 3222 Flyš
32222 Flyš in the basin of the Morava-the southern part of the base of the basin of the Morava 3222 Flyš
32230 Flyš in the catchment area of the northern part of the base weight-3223 Flyš in weight-northern part
32240 Flyš in the catchment area of the southern part of the base weight-3224 Flyš in weight-southern part
32301 Central Moravian Carpathians-the northern part of the base 3230 Central Moravian Carpathians
32302 Central Moravian Carpathians-the southern part of the base 3230 Central Moravian Carpathians
41100 4110 Police Police Base Pan Pan
42100 Hronovsko-poříčská base Hronovsko-4210 chalk poříčská chalk
42210 Podorlická chalk in the basin, including basic 4221 Podorlická chalk basin, including
and Metuje and Metuje
42220 Podorlická chalk in the catchment area of Eagle base 4222 Podorlická chalk basin Eagle
42310 Ústecká synklinála in the catchment area of Eagle base in the river basin synklinála 4231 Ústecká Eagle
42320 Ústecká synklinála in Svitavy basic 4232 Ústecká synklinála in Svitavy
42400 synklinála Excellent base 4240 Excellent synklinála
42500 Hořicko-miletínská base Hořicko-4250 chalk miletínská chalk
42610 Kyšperská synklinála in the catchment area of Eagle base Kyšperská synklinála basin 4261 Eagle
42620 Kyšperská synklinála-the southern part of the base synklinála-4262 Kyšperská southern part
42700 Vysokomýtská synklinála basic Vysokomýtská synklinála 4270
42800 Velkoopatovická chalk Velkoopatovická chalk base 4280
42910 Králický break-northern part of the base 4291 Králický break-northern part
42920 Králický break-the southern part of the basic "break-4292 Králický southern part
Mary C 43100 chalk base 4310 Chrudimská chalk
43200 Long bound-southern part of basic Long bound-4320 South part
43300 Long bound-north part of the base Long bound-4330 north part
43400 Čáslavská chalk base 4340 Čáslavská chalk
43500 Velimská chalk Velimská chalk base 4350
43600 Labská chalk base 4360 Labská chalk
44100 Jizerska chalk right-bank basic 4410 Jizerska chalk right-bank
44200 Jizerský usually top 4420 Jizerský usually
44300 Jizerska chalk left-bank basic 4430 Jizerska chalk left-bank
45100 Chalk North of Prague the basic Chalk 4510 North of Prague
45210 Chalk Creek Košáteckého base Košáteckého Chalk Creek 4521
45220 Chalk Liběchovky and Pšovky basic Liběchovky and Pšovky Chalk 4522
45230 Chalk and Úštěcký Creek Obrtky base Obrtky and Úštěcký 4523 Chalk Creek
45300 Roudnická chalk base 4530 Roudnická chalk
45400 Ohárecká chalk Ohárecká chalk base 4540
4550 45500 Holedeč basic Holedeč
46110 Chalk lower River after Děčín-left base 4611 Chalk lower River after Děčín-left
shore, South Shore, part of the southern part of the
46120 Chalk lower River after Děčín-left base 4612 Chalk lower River after Děčín-left
shore, North Shore, northern part
46200 Chalk lower River after Děčín-right base 4620 Chalk lower River after Děčín-genuine
shore bank
46300 Děčínský Sněžník basic 4630 Děčínský Sněžník
the upper Chalk is in charge of basic 46400 4640 Chalk Upper Ploučnice
46500 Chalk Lower and upper basic Ploučnice 4650 Chalk Lower and upper Ploučnice
Kamenice Kamenice
46600 Chalk Lower Sink and the base of the lower Chalk 4660 Křinice Kamenice and Křinice
47100 Basal coated collector on deep-sea 4710 Basal coated collector to
The Jizera River Jizera River
47200 Basal coated collector from deep-sea 4720 Basal coated collector from
The hammer of the hammer after the Elbe River after the river Elbe
47300 Basal coated deep Basal coated 4730 collector collector
in benesov in benesov synklinále synklinále
51100 Plzeňská pan base 5110 Plzeňská Pan
51200 5120 Manětínská Manětínská pan base Pan
51310 Rakovnická pan base 5131 Rakovnická Pan
51320 5132 Žihelská Žihelská base Pan Pan
51400 8 pan base 5140 8 Pan
51510 Podkrkonossky permokarbon basic 5151 Podkrkonossky permokarbon
51520 Náchod perm basic 5152 Náchod perm
51610 Dolnoslezská Pan-western part of the base Pan-5161 Dolnoslezská western part
51620 Dolnoslezská Pan-eastern part base 5162 Dolnoslezská Pan-eastern part
52110 Poorlický perm-northern part of the base 5211 Poorlický perm-northern part
52120 Poorlický perm-the southern part of the base perm-5212 Poorlický southern part
52210 Boskovice-northern part of the base 5221 Boskovice-northern part
52220 Boskovice-the southern part of the base 5222 Boskovice-southern part
61110 unique crystalline complex and Western base 6111 unique crystalline complex and the Western
part of the Ore mountains, part of the Ore mountains
61120 unique crystalline complex of the Slavkov forest base 6112 unique crystalline complex of the Slavkov forest
61200 unique crystalline complex in mezipovodí the Ohře River after basic 6120 unique crystalline complex in mezipovodí after the Ohře River
Kadan Kadaň
61310 unique crystalline complex Ore mountains from the base of the Ore mountains from the unique crystalline complex 6131
Chomutovka Chomutovka after Moldavu after Moldavu
61320 unique crystalline complex East of the base unique crystalline complex East of 6132
Erzgebirge Ore mountains
61330 Teplice Teplice 6133 riolith riolith base
62110 unique crystalline complex of the Bohemian Forest in the catchment area of the base 6211 unique crystalline complex of the Bohemian Forest in the catchment area
Kateřinského Creek Kateřinského Creek
62121 unique crystalline complex in May after the Silver base unique crystalline complex in the basin Can 6212 after Silver
and the Radbuza after Staňkov and Radbuza after Staňkov
62122 unique crystalline complex and Proterozoic basin in the basin base 6212 unique crystalline complex May after Silver
May after the silver, and after the Radbuza Staňkov-and the Radbuza after Staňkov
the upper part of the catchment of the Black Creek
62130 unique crystalline complex of the Bohemian Forest base 6213 unique crystalline complex of the Bohemian Forest
Black Creek basin in the basin of the Black Creek
62210 unique crystalline complex in mezipovodí May mezipovodí 6221 unique crystalline complex in the base Can
under the Silver under the Silver
62221 unique crystalline complex and Proterozoic the base 6222 unique crystalline complex and Proterozoic
the Úhlava River basin and the lower reaches of the Úhlava River basin and the lower reaches
Radbuza-western part of the Radbuza
62222 unique crystalline complex and Proterozoic the base 6222 unique crystalline complex and Proterozoic
the Úhlava River basin and the lower reaches of the Úhlava River basin and the lower reaches
Radbuza-eastern part of the Radbuza
62223 unique crystalline complex and Proterozoic the base 6222 unique crystalline complex and Proterozoic
the lower reaches of the Úhlava River basin and the lower course of the Úhlava Radbuza
62300 unique crystalline complex, Proterozoic and basic 6230 unique crystalline complex, Proterozoic and
paleozoikum in the catchment area of the Berounka river Berounka river basin paleozoikum
62400 Late silur and devon Barrandienu basic 6240 Late silur and devon Barrandienu
62500 Proterozoic and paleozoikum in the catchment area of the base and paleozoikum in 6250 Proterozoic basin
tributaries of the River Vltava Affluents of the River Vltava
63101 unique crystalline complex in the catchment area of the upper Vltava River basin base 6310 unique crystalline complex upper Vltava
and Czech and Czech
63102 unique crystalline complex in the catchment area of the upper Vltava River basin base 6310 unique crystalline complex upper Vltava
and the Czech Republic-Vltava River after the confluence and Úhlava
with the flow of the river Malše
Unique crystalline complex in the central basin 63201 basic 6320 unique crystalline complex in the central basin
The Vltava River-southern part of the Vltava River
63202 unique crystalline complex in the middle of the base in the central basin unique crystalline complex 6320
The Vltava River-upper basin of the vitriol of the Vltava River
Unique crystalline complex in the central basin 63203 basic 6320 unique crystalline complex in the central basin
The Vltava River Vltava River from the confluence of the Mezipovodí-Vltava River
with Vápenickým Brook after Slapy y
63204 unique crystalline complex in the central basin in the central basin unique crystalline complex 6320
The Vltava River-northern part of the Vltava River
64110 unique crystalline complex Bohemia uplands base 6411 unique crystalline complex Bohemia uplands
64120 unique crystalline complex Lusatian mountains base 6412 unique crystalline complex Lusatian mountains
64130 unique crystalline complex of the Jizera Mountains in the basin base 6413 unique crystalline complex of the Jizera Mountains in the basin
The Lusatian Neisse River The Lusatian Neisse River
Unique crystalline complex of giant mountains and Jizera 64140 basic 6414 unique crystalline complex of giant mountains and Jizera
the mountains in the basin of Jizera Mountains in the basin of Jizera
64200 unique crystalline complex of the orlicke mountains base 6420 unique crystalline complex of the orlicke mountains
Unique crystalline complex North of Eastern 64311 basic 6431 unique crystalline complex North of Eastern
Sudetenland-Southeast part of Sudetenland
Unique crystalline complex North of Eastern 64312 basic 6431 unique crystalline complex North of Eastern
Sudetenland-northwest part of Sudetenland
Unique crystalline complex South of Eastern 64321 basic 6432 unique crystalline complex South of the Eastern
Hitler The Sudetenland
64322 unique crystalline complex South of the Eastern base of South Eastern section 6432 unique crystalline complex
Sudetenland-Moravia after the confluence with the flow of the Sudetenland
The Moravian Sázava
64323 unique crystalline complex South of the Eastern base of South Eastern section 6432 unique crystalline complex
The Sudetenland – a celebration of the mouth into the flow of the Moravia of the Sudetenland – a celebration of the mouth to the flow of Moravia
65100 catchment area of the river Lužnice, basic unique crystalline complex in 6510 unique crystalline complex in the catchment area of the river Lužnice
65200 unique crystalline complex in Sázava basin base in Sázava basin 6520 unique crystalline complex
65310 unique crystalline complex basic 6531 Kutná Hora, the manufacturing of unique crystalline complex
65321 unique crystalline complex of the iron mountains-basic unique crystalline complex of the iron mountains-6532
the South-Eastern part of the
65322 unique crystalline complex of the iron mountains-basic unique crystalline complex of the iron mountains-6532
the north-western part of the
65401 unique crystalline complex in the catchment area of the Dyje river basin unique crystalline complex base 6540 Dyje
-Western part
65402 unique crystalline complex in the catchment area of the Dyje river basin unique crystalline complex base 6540 Dyje
-Eastern part
65500 unique crystalline complex in Jihlava in the basin base 6550 unique crystalline complex of Jihlava
65601 unique crystalline complex in the catchment area of the Svratka River basin unique crystalline complex base 6560 Svratka
-middle part
65602 unique crystalline complex in the catchment area of the Svratka River basin unique crystalline complex base 6560 Svratka
-After the junction with the Svitava Punkva flows
65603 unique crystalline complex in the catchment area of the Svratka River basin unique crystalline complex base 6560 Svratka
-Western part
65700 unique crystalline complex Brno Brno 6570 unique crystalline complex base unit
66111 Kulm Nízký Jeseník in the Odra river basin base 6611 Kulm Nízký Jeseník in the Odra river basin
66112 Kulm Nízký Jeseník in the Odra river basin base 6611 Kulm Nízký Jeseník in the Odra river basin
-the catchment area of Opava to the flow of the Odra
66120 Kulm Nízký Jeseník in the basin of the Morava basic 6612 Kulm Nízký Jeseník in the basin of the Morava
66200 Kulm drahany Highlands elementary 6620 Kulm drahany Highlands
66300 Moravian Karst base 6630 Moravian Karst
66400 Mladečský kras Karst base 6640 Mladečský
------------------------------------------------------------------------------------------------------------------------
1) Article. 2 (2). 1, para. 2, paragraph 1. 3, para. 4, para. 5, para. 6, art. 3
paragraph. 1, para. 2, paragraph 1. 3, para. 4, para. 6, art. 4 (4). 1, para. 2,
paragraph. 3, art. 5 (3). 1, para. 2, paragraph 1. 3, para. 5, annex I, II, III,
(IV) European Parliament and Council Directive 2006/118/EC of 12 July 2005.
December 2006 on the protection of groundwater against pollution and deterioration
State.
Annex II and in the directive of the European Parliament and Council Directive 2000/60/EC of the European
23 October 2000 establishing a framework for Community action in the
field of water policy.
Article. 4, art. 5, art. 6 of Commission directive 2009/90/EC of 31 March 2004. July
2009, which is in accordance with European Parliament and Council Directive 2000/60/EC
provides technical specifications for chemical analysis and monitoring of the State of
waters.
2) Decree No. 428/2001 Coll., implementing Act No. 274/2001 Coll.
water supplies and sewerage Act for public use and amending certain
laws (law on water supplies and sewerage Act), as amended by Decree No.
140/2004 Coll. and Decree No. 515/2000 Coll.
3) the agreement on the International Commission for the protection of the Elbe of 8 June. October 1990.
Communication from the Ministry of Foreign Affairs No. 122/1999 Coll., on negotiation of
The Convention on cooperation for the protection and reasonable use of the river Danube.
Communication from the Ministry of Foreign Affairs No. 2/2003 Coll. m. s., the agreement on the
International Commission for the protection of the oder.
4) Act 22/1997 Coll., on technical requirements for products and amending
and additions to certain laws, as amended.
5) § 23a para. 2 Water Act.
6) § 32, 33 para. 2 Water Act.
7) Government Regulation No. 103/2003 Coll., on the determination of vulnerable areas and the
the use and storage of fertilizers and manure, crop and střídaání
implementing anti-erosion measures in these areas, as amended by regulation
No. 219/2007 Coll. and regulation of the Government No. 108/2008 Coll.
for example, § 8) 30 to water Act 35.
9) section 22 of the Water Act.
10) Government Regulation No. 262/2012 Coll., on the determination of vulnerable areas and
the programme of action, as amended.
